planning for jamaica bay’s future: preliminary...
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Planning For Jamaica Bay’s Future:
Preliminary Recommendations on the Jamaica Bay Watershed Protection Plan
Submitted by the Jamaica Bay Watershed Protection Plan Advisory Committee
June 29, 2006
Photo Credits: National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004, March. The Evolving Legacy of Jamaica Bay. New York City Department of Environmental Protection. 2006, February 9. The Jamaica Bay watershed protection plan. Presentation at York College, Queens.
PLANNING FOR JAMAICA BAY’S FUTURE:
PRELIMINARY RECOMMENDATIONS ON THE JAMAICA BAY WATERSHED PROTECTION PLAN
Submitted by the Jamaica Bay Watershed Protection Plan Advisory Committee
June 29, 2006
Table of Contents
Part I
Introductory Note from the Committee……………………………………………………….1
Introduction……………………………………………………………………………. 1
An Oasis amid America’s Largest City…………………………………….…………. 2
Part II
Challenge: Degraded Water Quality…………………………………………………... 3
Water Quality Goals & Next Steps……………………………………………………. 4
Challenge: Compromised Ecology……………………………………………………. 10
Ecological Goals & Next Steps……………………………………………………….. 11
Challenge: Inadequate Planning & Outreach………………………………………….. 14
Planning and Outreach Goals & Next Steps………………..…………………………. 15
Appendix A: Local Law 71
Appendix B: Int. No. 376
Appendix C: Maps of the Jamaica Bay Watershed/Sewershed
Appendix D: List of Committee Members Including Affiliations and Biographies
Appendix E: List of Expert Panels Convened by the Advisory Committee
Appendix F: List of Watershed Protection Plan Goals
Appendix G: Local Law 86
Appendix H: Executive Order 111
Appendix I: Local Law 83
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PART I INTRODUCTORY NOTE FROM THE COMMITTEE These preliminary recommendations are submitted to the Speaker of the New York City Council and the Commissioner of the New York City Department of Environmental Protection (DEP) pursuant to Local Law 71 (See Appendix A). As enacted in 2005, Local Law 71 requires DEP to develop a Jamaica Bay Watershed Protection Plan to restore the water quality and ecological integrity of Jamaica Bay. Local Law 71 created the Jamaica Bay Watershed Protection Plan Advisory Committee to assist DEP in developing the plan; the law specifically charged the committee with developing its own recommendations concerning the plan by no later than July 1, 2006. On June 13, the original sponsor of Local Law 71 introduced legislation to extend DEP’s deadline for submission of the final plan by one year, from September 1, 2006 to September 1, 2007, as well as to provide for several interim milestones (See Appendix B). The legislation also calls for the committee to provide only “preliminary” recommendations by July 1, 2006, and to provide its final recommendations eleven months later, on June 1, 2007. The committee fully supports the proposed amendments to Local Law 71 and welcomes the opportunity to collect additional public and agency feedback on its work through the amended process. Accordingly, the recommendations contained herein are provided as both preliminary recommendations consistent with the pending legislation, and as recommendations consistent with the current law. The committee hopes for and anticipates the legislation’s passage so that it, and DEP, can continue their work in developing both a vision and workable solutions for Jamaica Bay’s future. INTRODUCTION
Jamaica Bay’s resources are in jeopardy. Thousands of acres of the bay’s marshlands are mysteriously disappearing. Scientists predict that, at the current rate, the marsh islands will completely vanish in less than twenty years.1 Poor, and in some places deteriorating, water quality remains a continuing problem for the bay, and may even be spurring the marsh loss.2
In response to this crisis, in 2005 the City of New York enacted Local Law 71. The new law calls for the
development of a watershed protection plan for the “watershed/sewershed” of Jamaica Bay. (See Appendix C.) The plan’s overall goal is “to restore and maintain the water quality and ecological integrity of Jamaica bay.”3
Local Law 71 also established a seven-member Jamaica Bay Watershed Protection Plan Advisory Committee (three members appointed by the city council and four members appointed by the mayor) to advise the New York City Department of Environmental Protection (DEP) in plan creation and to provide specific plan goals and recommendations to DEP and the New York City Council by July 1, 2006. (See Appendix D.) This report provides the committee’s recommendations, as required by the law, and explains the process the committee has gone through to formulate these recommendations.
Following enactment of Local Law 71, the committee met on a regular basis from November 2005 through June 2006. The committee spent the first few months after its appointment developing draft goals and recommendations focusing on specific measures as prescribed by Local Law 71. As set out in the law, these measures include: • Best management practices to minimize/control soil
erosion, reduce point and nonpoint source pollution (e.g. development practices that control and minimize stormwater)
• Measures to address threats to aquatic habitat (e.g. restoring natural features and water flows)
• Land acquisition, planning/development practices that encourage or discourage certain land uses
• Protocol for agency coordination • A public education program • Enhanced enforcement against polluters • Additional items developed by the committee.
Local Law 71 also called for the committee to assess the legal, technical, environmental and economic feasibility of possible plan measures and to develop a schedule, with interim and final milestones, to implement the plan’s measures and achieve the specific goals and methods for monitoring progress.
Since the beginning, the committee has viewed its role in the development of the watershed protection plan as independent of, but cooperative with, DEP. The committee has held monthly joint sessions with DEP, and regularly exchanged technical information and progress reports.
The committee has also considered the most current scientific information available on the problems confronting the bay. Expert panels were convened on the topics of stormwater and green building best management practices, wetland loss and water quality in order to gain greater knowledge of the issues facing
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Jamaica Bay and to explore new ways of reducing stresses on the bay. (See Appendix E.)
Finally, the committee has sought to involve the public as much as possible in the development of recommendations. The committee and DEP held public meetings at the start of the process in Brooklyn and Queens in January and February 2006. At the meetings, the committee and DEP provided an introduction to the law and the process that the committee would be following in developing its recommendations, and invited both oral and written comments. The committee received a large number of comments which are reflected in this report. AN OASIS AMID AMERICA’S LARGEST CITY
Jamaica Bay’s value to the city, the region, and the nation is immeasurable. Accessible to America’s most populated city by subway and bus, Jamaica Bay is a haven for wildlife and the millions of people who visit the area each year. Even with its panoramic backdrop of Manhattan’s skyscrapers and the rumble of planes taking off from adjacent John F. Kennedy International Airport, it is easy to get lost in the bay’s restful open space and waters and lush green marsh islands. Hundreds of species of birds soar across along one of nature’s expressways – the Eastern Flyway migration route – on the way to breeding grounds further north. Endangered and threatened species like peregrine falcons, piping plovers, and the Atlantic Ridley sea turtle call this area home, and the wetland fringes serve as important nurseries for more than 80 fish species.4
The bay comprises one of the largest and most productive coastal ecosystems in the northeastern United States, and includes the largest tidal wetland complex in the New York metropolitan area.5 Connecting to the Atlantic Ocean via the Rockaway Inlet, the bay is also an important component of the larger Hudson-Raritan Estuary, which contains the New York-New Jersey Harbor complex, one of the world’s most utilized systems of waterways. Jamaica Bay’s wetlands serve as flood protection and shoreline erosion control for the homes and businesses of the encircling neighborhoods. The Jamaica Bay watershed, which feeds the freshwater portion of the estuary, extends deep into Brooklyn, Queens, and Nassau County.
Made of glacial till left behind during the last ice age and shaped by erosion and wave action,6 the open water and wetlands portion of Jamaica Bay is approximately eight miles long, four miles wide and covers 26,645 acres,7 more than half of which is part of Gateway National Recreation Area’s (Gateway)
Jamaica Bay Unit.8 The National Park Service (NPS) administers Gateway, which was established by Congress in 1972 in an effort to preserve outstanding natural areas closer to major urban centers. Gateway offers a multitude of benefits for local residents and encompasses the largest collection of natural systems, wildlife habitats, historic and cultural resources, and recreational opportunities in the New York City/New Jersey metropolitan area. Three-fourths of Gateway’s Jamaica Bay Unit is water, marsh, and meadowland; the remaining upland areas include beaches, dunes, and forests.9
At the heart of the Jamaica Bay Unit is the Jamaica Bay Wildlife Refuge (Refuge), which covers 9,100 acres and is the only wildlife refuge accessible by subway.10 The Refuge, a state- and nationally-recognized important bird area, provides a variety of habitats for more than 325 kinds of waterfowl and shorebirds.11 Visited by nearly 20 percent of the continent’s species of birds every year, Jamaica Bay is considered one of the best bird-watching locations in the western hemisphere.12
The neighborhoods surrounding Jamaica Bay are home to more than five hundred thousand New Yorkers.13 The bay is bounded by Brooklyn and Queens on its northwestern and northeastern shores, Rockaway Peninsula (also part of Queens County) on its southern shore, and Hempstead, Nassau County, along a small section of the bay’s southeastern shore. Major neighborhoods within and bordering the bay include the Rockaways, Canarsie, Spring Creek, Starrett City, Howard Beach, and Broad Channel. Residents of these communities consider the waters, parks, and open space surrounding the bay “a sanctuary or haven from the stress of the city.” 14 The Changing Bay
Human actions over time have significantly changed the bay’s physical dynamics. Throughout the bay’s history, it has served such competing functions as providing food and recreation for local residents, and as a place for sewage effluent and solid waste disposal. High bacterial levels from waste disposal ultimately forced the closure of the once-vibrant shellfishing industry in 1921.15 Sections of the bay’s bottom were dredged in the early part of the 20th century as the city considered turning Jamaica Bay into a major commercial and industrial port.16 Although the port was never built, the dredged channels and pits continue to impact the bay’s water quality and ecology. Many marshes surrounding Jamaica Bay have been filled and tributaries drastically altered to accommodate residential, commercial and
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transportation needs. Construction of John F. Kennedy International Airport (JFK) alone decreased the surface area of marshland by 18 square kilometers.17
Stakeholder efforts have been active in the bay since the late 1970s, and in 2001 Gateway convened a blue ribbon panel of national experts to examine the bay’s alarming and perplexing marsh loss. The panel focused on the bay’s reduced sediment supply and suspension problems and recommended a number of additional studies and restoration projects, such as the Big Egg Marsh thin layer sediment spraying, to restore healthy marsh elevations. Following on the panel’s work, the Jamaica Bay Ecosystem Research and Restoration Team (JBBERT) investigated potential restoration sites in the bay, primarily around the periphery. Restoration activities are moving forward at a few of these sites, but most remain still on the drawing board. To date, efforts by government and academic institutions, as well as community and environmental groups, have resulted in an improved understanding of the bay and its problems, but only very limited – even if promising in some cases (such as recent salt marsh thin layer sediment spraying) – restoration activity. Over a century of urbanization with resulting pollution, dredging, and filling has caused the bay’s decline and it will take the combined engagement of all stakeholders to restore the bay. PART II In the following sections of the report, the committee has identified certain preliminary recommendations as priority items. These priority recommendations are found at the beginning of each section. Identification of priority recommendations was based upon several factors, including the importance of the recommendation in addressing the bay’s problems and whether significant decisions were pending that might foreclose addressing the recommendation at a later date. CHALLENGE: DEGRADED WATER QUALITY
From the 1970s to the 1990s, major investments to the city’s sewage treatment plants dramatically improved the water quality of Jamaica Bay, but significant problems remain. While dissolved oxygen levels throughout much of Jamaica Bay’s open waters have risen, these levels in Grassy Bay and certain other borrow pits, as well as in some tributaries, are often too low to sustain year-round marine life and healthy
biodiversity. At least seven highly toxic sediment sites exist in the bay.18 And since 1986, algae levels have been on the rise and water clarity in Jamaica Bay has declined more than 20 percent.19
The primary known culprits are combined sewer overflows (CSOs) and discharges of treated wastewater from the four city sewage treatment plants that encircle the bay (26th Ward, Coney Island, Jamaica, and Rockaway plants).20 A combined sewer system that carries sewage and stormwater runoff to the plants for treatment serves most of the communities surrounding the bay. Rainfall intensity as low as 0.15 centimeters per hour for 6.7 hours will exceed the limited sewer and plant storage capacity, causing overflow of untreated sewage combined with stormwater through numerous outfalls ringing the bay’s waters.21 Additionally, every day, the plants release approximately 300 million gallons of treated wastewater into the bay.22 The wastewater effluent contains thirty to forty thousand pounds of nitrogen each day, far too much nitrogen for the bay to assimilate.23 One estimate puts the removal capacity of existing marshes somewhere between a tenth and a fifth of the total nitrogen inputs.24 In certain places and times in the bay, the excess nitrogen creates a eutrophic environment, where an overabundance of organic matter in the water spurs the growth of algae blooms that decrease oxygen levels in the water as the algal organisms die off and decompose. Oxygen levels can dip so low that any aquatic life not able to swim away will die.25 Indeed, by default, Jamaica Bay itself has become part of the city’s wastewater treatment process – providing sinks for nitrogen, fine particulates, and biological oxygen demand – a practice which has taken its toll on the ecology of the bay.
The nitrogen-rich waters may also hinder the health of salt marsh cordgrass (Spartina alterniflora), which is essential to breeding fish and bird populations, and holds the bay’s sediments together.26 While the emergent part of cordgrass may be unaffected, the root systems are often disproportionately undersized and not capable of sustaining the cordgrass under conditions of physical stress, such as erosive forces during storms.27
The New York State Department of Environmental Conservation (DEC) has included Jamaica Bay on its Section 303(d) impaired water list since 1998 because of violations of water quality standards relating to pathogens, nitrogen, and oxygen demand.28 DEC’s list cites CSOs and wastewater as the primary causes of the impairment. Specifically, CSOs have been documented as causing localized exceedances of bacterial standards in Jamaica Bay tributaries during and after storm events. CSOs are also believed to be significant sources of both organic pollutants and metals – such as
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dioxins, various pesticides, PCBs, lead and mercury – into the bay.29*
Some areas of Jamaica Bay have separated storm and sanitary sewers whereby wastewater is directed to the plants and stormwater is sent directly out to the bay. While this system eliminates CSOs, the stormwater still contains pollutants. For instance, the Belt Parkway’s runoff contains pollutants from automobiles, including motor oil, engine coolant, brake dust and gasoline. JFK, which occupies more than 5,000 acres along the bay’s north shore and is ranked fifteenth in worldwide airport passenger traffic,30 discharges into the bay runoff contaminated with anti-icing and deicing compounds and other toxic chemicals drained from the large paved surfaces that form JFK’s network of runways and taxiways.
Together with CSOs and stormwater, past releases from industrial facilities and three closed landfills – Edgemere Landfill off Rockaway Peninsula and the Fountain and Pennsylvania Avenue Landfills in Brooklyn – have significantly contributed to contaminant loading in the sediments of Jamaica Bay.31 Delays in the bay's flushing time caused by human alterations to the water flow (from dredging, filling, development) have increased the potential for pollutants to settle out to the bottom.32 Flushing time (or residence time) is simply the amount of time it would take for a particle of water (or contaminant) to circulate through the bay, i.e. from start to finish. Many of the toxic contaminants are persistent in the environment with the potential to accumulate through the food chain in the tissues of plants, invertebrates, fish and birds.33 CSOs and stormwater outfalls also add to the bay’s “floatables” – water-borne litter and debris like plastic bags, cigarettes, drink containers, and food wrappers.34
Finally, current treatment plant technologies do not screen out hormone disrupting chemicals from wastewater. Recent studies have revealed that trace substances with hormone-like properties from prescription and over-the-counter drugs, and chemicals from soaps and other products exist in treatment plant effluent, and could be accumulating in the sediments of receiving waterbodies.35 For example, estrogen from pharmaceuticals and industrial detergents that break down into products that mimic the hormone estrogen * DEC removed Jamaica Bay, as well as certain other New York City waterbodies, from the Draft New York State 2006 303(d) List of Impaired Waters Requiring a TMDL based largely on actions to be undertaken pursuant to several DEC-DEP consent agreements. The committee strongly opposes this proposal as, among other things, these agreements do not call for achieving water quality standards.
can contribute to higher levels of estrogen-like materials in treatment plant effluent. These chemicals can build up in the sediments and affect development of marine life, such as winter flounder, by depressing the male to female ratio, causing delayed development and reduced hatch and survival rates.36
To secure a healthy environment for Jamaica Bay’s wildlife and increased recreational opportunities for visitors, Jamaica Bay’s water quality must be further and significantly improved. WATER QUALITY GOALS & NEXT STEPS
Summary of Water Quality Recommendations
Increasing the nitrogen removal capability of Jamaica Bay’s sewage treatment plants will reduce algal blooms and thereby diminish the frequency and duration of anoxic events. The 26th Ward and Jamaica sewage treatment plants should be upgraded to tertiary treatment to screen out more nitrogen. It should also be investigated whether such tertiary treatment can remove possible endocrine disrupters and other byproducts of the modern post-industrial age. Additionally, centrate process effluent should be treated for reuse or discharged in a city area with better tidal flushing. Specifically, dewatering is the final step in the treatment plant process that wrings out the residual thickened organic matter or sludge; the wastewater from this process is nitrogen-rich and called centrate.37 Centrate is run back through the plants’ systems to help reduce its nitrogen level, but it still contributes to higher overall nitrogen releases from the plant.38 The Jamaica plant usually dewaters its own sludge; the 26th Ward plant dewaters sludge from Coney Island, Rockaway, and sometimes the Jamaica and Owls Head plants.39
Reduction and eventual elimination of CSOs will require a multi-pronged approach. Increasing the system’s wet weather holding capacities and system maintenance will decrease CSO occurrences and contribute to cleaner waters with less organic content. Cleaning out sewer lines to remove accumulated sediment will enhance storage capacity immediately.
It remains important that DEP continue to site, design, and construct adequate CSO storage capacity, particularly for areas in the watershed/sewershed in which this is the only or principal CSO abatement option available. But constructing additional retention tanks on a diminishing land base and increasing sewer storage will not be enough to eliminate the CSO problem. It is becoming increasingly clear that simply building huge storage tanks to capture for eventual
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treatment all of the ever-expanding wastewater and the stormwater will need to be augmented with other strategies – on a citywide basis, by DEP’s own calculations, the currently planned suite of CSO storage tanks will barely keep pace with the city’s currently projected development patterns.40 In other words, DEP’s planned projects will not improve overall water quality, but will simply prevent it from getting worse.
It is vital to move solutions to the CSO problem up into the watershed/sewershed and closer to the problem’s source. Stormwater best management practices (BMPs) can diminish water flow to the plants (e.g. through increased conservation methods and incentives) and delay and/or reduce stormwater flow into the sewer system (e.g. through increased plantings that encourage infiltration and minimize runoff from pavement and other impervious surfaces directly to sewers), reducing the deluge of water that overwhelms the sewage system’s holding capacity. Preliminary modeling conducted by DEP indicates that implementation of BMPs in the watershed/sewershed could result in a significant reduction in the number and severity of CSO events in Jamaica Bay.
DEP has suggested that a long-term solution to the CSO problem include a weakening of water quality standards for certain waterbodies.41 The committee strongly discourages this “move the goalposts” approach. The goal of “fishable and swimmable” water for Jamaica Bay and its tributaries should not be changed. The bay deserves and requires this standard of performance, as do the communities that rely on and enjoy these waterbodies.
In addition, at various times in the past, the relocation of a portion or all of the bay’s sewer and stormwater outfalls out into the Atlantic Ocean has been proposed. While this plan would reduce contaminated waters entering Jamaica Bay, given circulation patterns and tidal flows, some fraction of the nitrogen-rich effluent discharged from the pipe would eventually end up back in the bay and in New York Harbor.42 The relocation scheme would also remove the largest source of freshwater into the bay.43 Currently, only 10 percent of the bay’s freshwater input is through groundwater.44 It is the Advisory Committee’s opinion that this option should continue to be studied, but that tertiary treatment for the 26th Ward and Jamaica sewage treatment plants and stormwater BMPs must first be implemented and the results monitored. The committee believes that the technical and legal difficulties associated with outfall relocation are likely to be insurmountable, and recommends converting the Jamaica Bay watershed into a showcase for state-of-the-art sewage treatment
and green technologies. The committee also recommends examining additional connections for flow of ocean water to the back bay through an open cut in the form of a stabilized inlet or through a series of underground chambers or culverts. In addition to the enhanced flushing of the back bay’s waters, such a connection to the Atlantic Ocean may provide a source of additional sediment; a lack of sediment is considered to play a role in the salt marsh loss problem. This connection may also provide renewable energy opportunities.
Policies should be put in place to prevent and reduce contaminated sediment in Jamaica Bay. In addition to eliminating CSOs and stormwater inputs with high pollutant loads, removal of major CSO sediment and past industrial deposits should be examined in order to improve the bay’s water quality and wildlife health. Monitoring of other contaminated areas is needed to assess impacts and, as needed, treat or isolate these risks.
Restoring vibrant shellfish populations to the bay could also improve overall water quality, as well as potentially provide recreational benefits through harvesting (depending on contaminant levels) and improved fishing. Oysters filter out contaminants and their colonies form natural reefs that provide fish habitat. In the latter part of the 19th century, Jamaica Bay was celebrated for its shellfish, including the eastern oyster, known then as the Rockaway oyster. Nearly 450,000 tons of oysters and clams were harvested from Jamaica Bay in 1906, but pollution, decreasing habitat, and overharvesting caused the industry to crash less than twenty years later.45 NY/NJ Baykeeper has created a volunteer-driven oyster gardening program to restore oysters throughout the Hudson-Raritan Estuary, and similar efforts should be launched in Jamaica Bay.46
Improved trash removal would make a difference in the bay’s appearance and water quality. Dedicating a skimmer boat to Jamaica Bay and increased trash receptacles and pick up capacity would reduce marine debris, and bayfront property owners should be required to keep their shorelines clean. Specific Water Quality Goals & Recommendations Goal: Secure fishable/swimmable waters in
Jamaica Bay. Meet or exceed current federal, state, and local
water quality standards for Jamaica Bay’s open water and tributaries. Attaining these standards would at least ensure water suitable for secondary recreation (e.g. kayaking, fishing) in most of Jamaica Bay’s waters, and
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primary recreation (e.g. swimming, shellfishing) in the bay’s open waters.
Significantly reduce the frequency and severity of harmful algal blooms in Jamaica Bay’s open waters resulting from anthropogenic influences.
Reduce inputs of nitrogen and organic substances into Jamaica Bay to levels necessary to achieve numeric water quality criteria for dissolved oxygen (5.0 milligrams/Liter) throughout Jamaica Bay’s open waters.
Significantly reduce combined sewer overflows (CSOs) with the goal of eliminating all CSOs into Jamaica Bay (including tributaries) by 2020.
(See Appendix F for a list of all watershed protection plan goals.) Recommendations to meet the goal of securing fishable/swimmable waters: Upgrade and maintain sewage treatment plants and the sewer system
Priority recommendation: Upgrade the 26th Ward and Jamaica wastewater treatment plants to tertiary treatment to reduce nitrogen inputs into the bay. Right now, sewage is screened for floatables (preliminary treatment), biologically treated to reduce the wastewater’s organic content (primary and secondary treatment), and disinfected with chlorine. Adding tertiary treatment would further remove nitrogen from the continuous effluent stream released into Jamaica Bay, and may assist in screening out endocrine disrupters. Both plants have nearby vacant property which could accommodate these new facilities. DEP pilot projects utilizing the nitrogen capture technologies of SHARON (single reactor system for high activity ammonium removal over nitrite), which uses biological methods to convert ammonia to nitrogen gas, and ARP (ammonia recovery process), which uses physical methods to convert ammonia to commercial fertilizer, should be carefully reviewed for possible adoption in the bay and fast-tracked.47
Priority recommendation: Stop centrate processing
at Jamaica Bay’s sewage treatment plants or further treat centrate for nitrogen removal. DEP analyses show that removing 26th Ward centrate processing alone would result in a decrease of 2,170 pounds of nitrogen per day – approximately a six percent reduction in total daily nitrogen
loading to the bay.48 The Advisory Committee believes that centrate treatment at the 26th Ward and Jamaica plants could be better handled through reuse or by treating at other city plants that discharge into waters with more efficient discharge rates, rather than into Jamaica Bay.49
Explore alternative treatment plant disinfection
methods. Conventional chorine treatment results in the formation of chlorinated organic compounds in plant effluent; such chlorinated compounds are increasingly considered to be environmentally harmful. Ultraviolet (UV) and ozone are two alternate methods of disinfection that should be considered.
Revise JFK’s State Pollutant Discharge
Elimination System (SPDES) permit. This permit has not been significantly modified since it was first issued in 1987 and it no longer meets Environmental Protection Agency and state regulatory requirements. A draft permit was recently released for public comment. The final permit should incorporate requirements for monitoring and stormwater pollution prevention planning, and include effluent limits that ensure that the permit fully protects Jamaica Bay’s water quality from harmful contaminants in the airport’s runoff.
Develop and implement strategies to trap initial
stormwater runoff, known as the “first flush,” in communities that are separately sewered. Initial runoff is usually more polluted than runoff originating later on in a storm event and such strategies can prevent high pollutant loads from reaching the bay. A first flush collection system can capture the most polluted stormwater during a rain event for treatment and allow for less polluted stormwater discharges.50
Use natural resource damage (NRD) assessment
procedures to impose fines for illegal discharges to the bay that could have been avoided by proper maintenance, and create a dedicated fund for restoration programs arising from these claims. During New York City’s 2003 power failure, backup generators at two sewage treatment plants failed, causing thirty million gallons of untreated sewage to spill into the East River51 and more than two hundred and thirty million gallons to spill into the Hudson River.52 DEP’s inadequate backup generator maintenance and the resulting sewage discharges violated federal and state laws.53
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Harsher sanctions would help reinforce the importance of proper maintenance and timely repairs.
Identify chemicals in treatment plant effluent
which may have harmful ecological effects, such as components from pharmaceuticals. Characterize the levels and amounts of such chemicals entering Jamaica Bay and implement treatment and/or pre-treatment measures as necessary.
Clean out accumulated sediments in sewer lines
and catch basins to enhance their water storage capacity, and schedule regular cleanings to remove debris. Sewer lines and catch basins are the bay’s first defense against oil, grease, trash and organic matter in stormwater – the cleaner these routes to the plants are, the more room they have to hold their full capacity of water and prevent CSOs. Where possible, these structures should be visually marked to increase public awareness of their purpose.
Restore tributaries leading into Jamaica Bay.
Improving these water corridors could help increase the natural flow of water and sediments to the bay, and reduce the impact of CSO events.
Review DEP’s portfolio of industrial pre-treatment
permittees within the Jamaica Bay watershed with the goal of instituting BMPs with respect to their industrial processes in order to reduce loading of harmful chemicals in the influent to the treatment plants and ultimately in what is discharged to the bay.
Adopt stormwater BMPs
Priority recommendation: Revise codes, guidelines and requirements that govern construction, reconstruction and landscaping of the city’s public infrastructure, including sidewalk, street, median and public spaces, to incorporate minimum standards of performance for stormwater retention and infiltration. Over the last decade, advances in technologies and a first wave of applications around the country have made certain BMPs for stormwater appropriate for widespread use in the public infrastructure. For the Jamaica Bay watershed/sewershed, measures to increase infiltration hold particular promise, as many (although not all) parts of the bay’s watershed/sewershed have a low groundwater table. For example, both urban and suburban areas in Pennsylvania and Michigan have used porous
asphalt pavement successfully to increase infiltration and decrease stormwater runoff. Porous asphalt makes use of stone aggregates that are fine enough to allow water infiltration into an underlying stone bed, allowing the removal of suspended solids, metals, oils and grease at very high rates.54
Priority recommendation: Implement a city pilot
program that aggressively tests a variety of stormwater BMPs (e.g. green strips/medians, enhanced curb designs, use of porous sidewalk pavement) including through one or more area-specific pilot projects within the watershed area in both Brooklyn and Queens that would maximize use of such BMPs. Monitor and adapt the projects to generate a better base of information on the efficacy of different BMPs. For example, Seattle’s Street Edge Alternative (SEA) project, which replaced impervious surfaces with porous materials, added vegetation along streets to enhance natural drainage and narrowed streets to reduce runoff, showed that stormwater BMPs are feasible in a large, metropolitan city. The SEA project’s success led to its expansion throughout the city, and so far has reduced stormwater discharge in project areas by a factor of ten.55 Actual implementation and monitoring of these types of projects, rather than lengthy modeling exercises, is also important, as experiences across the country have frequently shown that benefits are greater upon implementation than had been initially calculated.56 Such pilot projects also have educational and public awareness value.
Create a list of city-approved stormwater
runoff/pollution BMPs for buildings and associated landscaping, and encourage their adoption by eliminating barriers in city building codes against their use, providing incentives to private developers who adopt BMPs (e.g. perhaps offering a reduced water rate) and requiring a certain percentage of city-funded new and redevelopment projects to incorporate BMPs. A review of city building codes to eliminate any barriers to stormwater BMPs should be conducted as soon as possible. The city has already begun promotion of green building technologies with Local Law 86, which requires new city construction to qualify for the U.S. Green Building Council’s Leadership in Energy and Environmental Design (LEED) silver certification.57 (See Appendix G.) This requirement should be incorporated into all
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agreements dealing with real estate property which the city leases to others for development as well. Further, the city should consider adopting the following standards/incentives to reduce inputs into the sewer system: require publicly financed buildings to devote a portion of their roofs for vegetated cover, increase the availability of green tax credits that private developers can use for green building technologies, and compel new tenancies on city-owned property requiring new buildings or substantial renovation of existing buildings to comply with Executive Order 111. (See Appendix H.) With approximately 300,000 square feet of green roof space constructed in 2005, Chicago is generally recognized as the current leader among American cities in green roofs.58 New York City should aspire to take over this ranking over the next five years; the large number of industrial and/or commercial establishments with significant roof areas in the bay’s watershed/sewershed should make it a prime area for such a focused effort by the city.
Conserve water
Priority recommendation: With the goals of reducing water waste and lessening the impact on sewer systems, require that the city implement an aggressive public education program and a system of requirements and incentives to decrease residential and industrial water use in the Jamaica Bay sewershed by 15 percent within 10 years.59 Reducing the amount of water entering treatment plants will both increase plant capacity during storm events and allow for an increase in the residence time of wastewater in the plant, aiding in the implementation of nitrogen removal technologies. New York City’s sewage has been described as weak; therefore, water conservation efforts should not increase the concentration of sewage solids to the point of causing treatment difficulties.60 Previous city water conservation efforts aggressively focused on leak detection and repair, replacement of old toilets with water efficient ones, installation of water meters and education about efficient water use. Largely thanks to these programs, New Yorkers decreased their water consumption by 25 percent from 1988 to 2001, but more can be done.61 Approximately 14 percent of household water is still wasted due to faucet leaks and drips, running water, and toilet seepage, among other causes.62 It has been almost a decade since the last major public campaign to increase water conservation, and, given this
amount of time and recent technological advances, it is time for a renewed push.
Goal: Significantly reduce harmful impacts from
soil and sediment contamination in Jamaica Bay.
No localized or net increase in contaminant concentrations in sediments and soils within Jamaica Bay watershed as a result of inputs via groundwater, combined sewer overflows, and water pollution control plant effluents.
Significantly reduce or reverse acute and chronic detrimental biological and ecological impacts from sediment and soil contamination within the Jamaica Bay watershed, focusing on known bioaccumulative agents, such as heavy metals and certain organic compounds.
Identify and monitor location and nature of sediment contamination in Jamaica Bay watershed. Prioritize remediation of sites containing sediments and/or soils identified as posing a human and/or ecological risk.
Recommendations to meet the goal of significantly reducing harmful impacts from soil and sediment contamination:
Designate Jamaica Bay as a “no discharge zone.” Establishing Jamaica Bay’s waters as a no discharge zone would prohibit any vessels from dumping treated or untreated waste into the waters. As an adequate number of waste disposal “pump out” stations would be required before this change could legally be approved; an analysis of the current number of recreational vessels against the number of pump out stations should be conducted.63
Pass legislation prohibiting the use of treated or
untreated contaminated sediment materials from outside of Jamaica Bay for restoration activities within the Jamaica Bay watershed. Existing Jamaica Bay sediments can be moved throughout the bay or clean sediments similar in grain size and sediment type to existing sediments can be used for filling activities within the bay, but any materials treated or untreated that would be characterized by their nature as in need of disposal should not be placed in Jamaica Bay.†
† One committee member dissents from this view believing that there is insufficient funds and clean material to restore all the pits in the bay and that the careful use of contaminated material as the sub-fill, above which a thick layer of clean material would isolate the contaminants, is not only technically feasible and safe, but
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Establish for Jamaica Bay the right of first refusal
for any navigational or construction-related dredged bay floor sediment. In instances where sediments are dredged from the bay, for example in Rockaway Inlet, the potential beneficial use for these sediments within Jamaica Bay should be considered before their uses elsewhere.
Comprehensively identify the toxic organic
compounds, including pesticides, and metals in CSOs and stormwater entering the bay and develop strategies for reducing and eliminating harmful inputs. In the limited research conducted to date, DEC’s Contaminant Assessment and Reduction Program has identified possible significant levels of toxic compounds in certain CSOs entering the bay.64 This research should be expanded and solutions to any problem sources identified.
Develop standards for identifying toxic sediment
areas within the bay and assess and prioritize the need for their removal, isolation and/or treatment based on whether or not these areas will erode over time or impact the water column. Toxic sediments should be classified as those that may pose a human health hazard and those that may impair the ecological and biological functioning of the ecosystem. Identify pilot projects to safely reduce the risks caused by these hot spots.
Examine the sources and impacts of airborne
contamination to Jamaica Bay. The New York Academy of Sciences Harbor Consortium found that airborne pollution plays a major role in the level of mercury found in New York-New Jersey Harbor waterways; other airborne contaminants may also be impacting Jamaica Bay.65
Goal: Restore populations of oysters and other
shellfish to Jamaica Bay. Recommendations to meet the goal of restoring oyster and shellfish populations:
Develop and implement a Jamaica Bay shellfish remediation and management plan to secure the long-term revitalization of oysters and other local shellfish for improved water quality, biodiversity
also provides a very cost-effective means of restoring pits in a low-funding environment and should not be ruled out without further study.
and public consumption while safeguarding human health.
Examine the possibility of creating one or more
reefs to serve as fish and shellfish habitat, and potentially as a diving ground for recreational users, in appropriate locations within the bay.
Goal: Eliminate floatables, debris, slicks and
settleable solids in Jamaica Bay to create a healthy, trash-free recreation area.
Eliminate discharge of CSO settleable solids into Jamaica Bay.
Remove CSO sediment deposits to help restore healthy marine ecosystems.
Identify and remove existing debris causing ecological or aesthetic impairment.
Recommendations to meet the goal of eliminating floatables, debris, slicks and settleable solids:
Dedicate a skimmer boat to Jamaica Bay clean up. A shallow draft pontoon-type skimmer vessel powered by two four-cycle outboard motors with a detachable height pickup net is needed to remove the floatable debris from Jamaica Bay’s waters. The boat should be designed to move quickly through the bay to collect and drop off trash, but also be able to navigate the shallow waters.
Remove, treat or isolate CSO sediment deposits
where appropriate, for example from Paerdegat Basin. As a result of continued CSO discharges, Paerdegat Basin has a mound of settled solids extending approximately 1,000 feet south from the basin’s head, 12 to 13 feet deep in areas. At the current accumulation rate, parts of the mound could be exposed during low tide within ten years. Such sediments and accompanying field conditions have an unpleasant odor and create hypoxic or anoxic conditions, and should be addressed immediately.66
Increase trash receptacles and collection in the
Refuge’s off-season. After Labor Day, most of the trash receptacles are removed throughout the Refuge, as NPS’ funding for trash collection is reduced. Exploring the use of animal-proof containers and solar-powered trash compactors, such as the “Big Belly,” which can hold trash for longer periods of time, or possibly negotiating additional disposal options with the New York City Department of Sanitation might allow for increased receptacles or more frequent trash pick up during the off-season.67
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Develop an “Adopt a Waterfront” effort that
allows private and public interests to be responsible for keeping areas of the bay clean. Similar efforts have been made in the city parks with the Partnerships for Parks program, which can serve as a model for Jamaica Bay.68
Develop city codes requiring Jamaica Bay
waterfront property owners – public and private – to keep their shorelines clean of floatable debris. Similar to how adjacent property owners currently must keep sidewalks clean, bayfront owners could be responsible for removing the refuse that collects on their land.
Develop a permanent and ongoing program for
collection and removal of large-scale debris visible above the high tide mark that has been demonstrated to affect aesthetic or ecological uses within the bay.
Support the passage of an expanded New York
State bottle bill, “The Bigger, Better, Bottle Bill.” An extension of current returnable container deposit laws to cover non-carbonated beverages, such as bottled water, fruit juice, and teas, would reduce the number of bottles entering the waste stream and found as litter across the city’s streets and waterways. The current bill would also require bottle distributors to transfer unclaimed deposits to the state’s Environmental Protection Fund.69 Since 1982, when the city passed its current returnable container deposit law, more than 80 million bottles and cans have been recycled.70
CHALLENGE: COMPROMISED ECOLOGY
One of Jamaica Bay’s most pressing threats is the rapid disappearance of its wetlands. Between 1924 and 1999, more than 50 percent of its marshes disappeared.71 And since the 1970s, marsh loss has accelerated, first to an average of 26 acres per year between 1974 and 1994, and more recently to an average of 44 acres per year between 1994 and 1999.72 Scientists currently predict that the bay’s marsh islands will cease to exist by 2024.73
Increasingly, marsh loss is occurring within the interior of marsh islands. When tidal pools expand, marsh areas become fragmented as the vegetation, largely cordgrass, S. alterniflora, becomes waterlogged and drowns, loosening the root structures that hold the land in place and turning into unvegetated mudflats.74
On some islands, more than 75 percent of the vegetation has disappeared in the past three decades.75
The exact cause or causes of Jamaica Bay’s wetlands degradation are still unknown. Even without further increases in mean sea level, at the current rate of loss, much of the wetlands are expected to erode.76 Ongoing investigations have focused on changes in sediment deposition and excessive sulfides in sediments caused by water pollution.
A hardening of the bay’s perimeter has made it more difficult for sediment to enter the bay by washing over land and has lowered the bay’s sediment budget (the amount of water-borne sediment available for deposition onto land).77 Without new sediment washing up on the marsh islands, these lands erode and vanish. Changes in the bay’s physical contours by westward progression of the Rockaway Peninsula, the dredging of navigational channels, the stabilization of Rockaway Inlet, the bulkheading of tributaries, landfills, and the construction of JFK and its runway into the bay – all have reduced sediment transport or affected water circulation. Hardened shorelines have also removed the natural graded edge between habitats, which is often the most productive strip.
Borrow pits and other areas from which sandy sediment was dredged to construct JFK and other areas around the bay and establish navigation channels may be acting as sediment sinks, and the increased wave energy and sediment flushing time caused by a deeper average depth may affect sediment accretion.78 The flushing rate/residence time for water to circulate throughout the entire bay is around 35 days;79 however, the specific residence time of water varies in different sections of Jamaica Bay – Grassy Bay with its deep borrow pits, for example, has a residence time of roughly one week.80 Changes in hydrology also affect the bay’s salinity and, if significant enough, can make the bay unsuitable for many of its current species of flora and fauna.
Recent research comparing accretion rates to marsh loss have suggested that a lower sediment budget may not be the primary cause – instead, water pollution may play the key role. High amounts of organic content from wastewater and CSOs in the bay may be contributing to high concentrations of sulfide; longer periods of flooding also lead to a gradual build up of hydrogen sulfide in sediments. S. alterniflora has limited ability to oxygenate its roots and detoxify sulfide. At high sulfide concentrations, it cannot recover; its roots degrade, marsh grass loss occurs and the marsh begins to lose its physical integrity and fragments.81
Other factors are exacerbating marsh loss. The bay’s remaining natural uplands serve as important
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buffers in maintaining the bay’s wetlands, reducing stormwater flow, and providing habitat corridors, but too many are neglected and being lost to development.82 Additionally, snow geese graze and trample on S. alterniflora. When marshes were more plentiful this did not pose a serious problem, but as the wetlands disappear, the geese’s impacts increase.83 Mussel banks block the natural drainage channels of the marshes, allowing ponds to form on marshlands and immersing S. alterniflora for longer periods each year.84 Tides bring wrack (sea lettuce, straw, dried seaweed, and floatable debris) into the bay to rest over the marshes and smother the remaining S. alterniflora.85 There is also the possibility that nitrogen-enriched water is causing an excessive growth of Ulva sp. (sea lettuce), which is carpeting the bay’s bottom and preventing sediments from being resuspended into the water for redistribution onto the marsh surfaces.86
Historically, the bay’s sediment accretion rate has kept pace with sea level rise and local subsidence.87 However, global climate models predict an increase in average sea level rise, which would exceed the historical accretion rate of the bay, leading to more frequent inundation of the marshes, wave action and marsh erosion, thereby potentially transforming them to mudflats.88 In research conducted for the U.S. Global Climate Change Research Program, a number of sea level rise projections were compared with plausible rates of marsh growth; analysis suggests that if enough sediment were available to marshes, the wetlands could survive all but the most extreme cases of future sea level rise.89
In addition to habitat loss, Jamaica Bay’s natural ecology is threatened by non-native and/or invasive species that out-compete indigenous species, as they often do not have naturally existing predators to check their proliferation. S. alterniflora provides food and shelter for birds, diamond-backed terrapins, and other animals and its detritus supports the salt marsh food chain.90 Large stands of common reed or Phragmites are overtaking disturbed wetlands and uplands, and driving out S. alterniflora without providing the same set of ecological functions.91 Other very aggressive invasive plant species, including Japanese knotweed, Japanese honeysuckle, Oriental bittersweet, Russian olive and mugwort, are decimating entire plant communities around Jamaica Bay and drastically reducing biodiversity.
Two hundred fourteen species within the bay have been designed as being of “special interest” by the U.S. Fish and Wildlife Service. These include several federally-designated threatened or endangered bird species, such as the piping plover, peregrine falcon,
and roseate tern. Plant species of note include seabeach amaranth, seabeach knotweed, and willow oak. The endangered Atlantic Ridley and loggerhead sea turtles travel through here, as do more than 80 species of fish, including winter flounder and Atlantic silversides.92 These native species need additional protection to thrive.
Jamaica Bay has not been afforded the level of protection warranted by its unique ecological resources. It is also important that efforts to restore lost habitats not wait for definitive answers to all the questions about the marsh loss problem; rather, in order to ensure Jamaica Bay’s continued viability, areas must be restored and protected simultaneous with ongoing investigations. Action is needed to protect and restore the bay’s wetlands and uplands, and its native species, before it is too late. ECOLOGICAL GOALS & NEXT STEPS
Summary of Ecological Recommendations The Jamaica Bay watershed extends far beyond the bay’s shoreline, and greater awareness of this fact and care of the resources therein is critical to revitalize the open water and wetlands portion.93 Protecting upland green areas and reclaiming vacant land for use as parks and other ecological buffers allows increased capture of stormwater through pervious surfaces, provides additional habitat for indigenous species and serves as additional buffer when located adjacent to wetlands or other natural areas. These small “green islands” within a concrete landscape also provide restful space for New Yorkers. Assuming continued positive results from current projects, Jamaica Bay’s inner salt marshes should continue to be stabilized by sediment placement to simulate the compromised natural sediment transport process. Building up the marshes’ sediment edge and preventing further deterioration will help maintain the bay’s wetlands in the face of sea level rise and ensure a home for the area’s wildlife. Developing a plan to address the growing challenge of invasive species in Jamaica Bay is essential to maintaining and improving the area’s native plant and wildlife diversity. Improving natural habitat through restoration activities will also benefit the diversity and numbers of native species. Specific Ecological Goals & Recommendations Goal: Prevent additional loss, in quality and
extent, of existing Jamaica Bay wetland and
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maritime native habitat complexes, including those serving as upland buffers, and increase the spatial extent of these habitats.
Recommendations to meet the goal of preventing additional loss of wetland and maritime native habitat complexes, and increasing their size:
Priority recommendation: Expeditiously transfer city-owned wetlands and adjacent areas within the Jamaica Bay watershed/sewershed to a responsible public agency, per the recommendations of the Wetlands Task Force created by Local Law 83 (a seven-member group to “inventory city-owned wetlands in the City of New York).94 (See Appendix I.) The Advisory Committee recommends that the wetlands and adjacent areas identified by the Task Force within the Jamaica Bay watershed be protected from development immediately.
Priority recommendation: Expand the buffer zone
on tidal wetlands in Jamaica Bay from 150 to 300 feet. The DEC requires a permit for most activity in the area adjacent to tidal wetlands extending 300 feet;95 however, in New York City, the adjacent area is defined to include only up to 150 feet. This definition should be changed to ensure protection of the city’s ever-shrinking number of wetlands. Shoreline buffer zones are very effective in filtering pollutants and excess nutrients and providing erosion and flood control, sediment trapping, and wildlife habitat.96 Furthermore, as apparent sea level rise continues due to local subsidence and global warming, landward migration of wetlands is inevitable and needs to be accommodated through expanded buffer zones.
Priority recommendation: Implement a Transfer of
Development Rights (TDR) program in the Jamaica Bay watershed to encourage the preservation of existing open space. TDR programs protect open space by allowing landowners in conservation zones to be compensated by selling their development rights for a particular parcel of land to the municipality or developers in another district. TDRs have proven successful in the Pine Barrens on Long Island and the Pinelands in New Jersey by limiting development of ecologically important areas while providing for growth in compatible areas.97 New York City has already instituted TDR programs as part of the Landmakers Preservation Ordinance and Broadway theater district.98
Evaluate the utility of a state or other formal
designation that capitalizes on the history and natural resources of Jamaica Bay. Signage throughout the watershed would increase public understanding of the role that upland areas, as well as wetlands, have on the bay. Enhanced use of BMPs could also be encouraged within the area.
Review additional vacant city-owned waterfront
properties which may not have been identified by the Wetlands Task Force to evaluate returning these areas to a more natural state, including through transferring them to the appropriate city agency for such purpose. For example, transferring and restoring natural areas on the east side of Thurston Basin would provide additional bay access for the Queens community. Indeed, the headwaters of Thurston Basin in Idlewild Park and environs are Jamaica Bay’s most pristine. The intact salt marsh and tidal creeks in the Idlewild Park area should be targeted for restoration activities, and there should be an effort to expand the spatial extent of this unique portion of Jamaica Bay’s watershed.
Revise New York City’s Waterfront Revitalization
Plan, as authorized by the New York State Department of State Coastal Zone Management Plan, to be consistent with the Advisory Committee’s recommendations.99 Zoning changes should be formulated and adopted as necessary to provide compatible uses within the bay environment while creating upland buffer areas and increased tidal wetlands adjacent to the bay through more stringent setback and building density requirements.
Goal: Protect Jamaica Bay’s inner salt marsh
complexes from additional loss of spatial extent and function, and increase the spatial extent of these marsh complexes.
Recommendations to meet the goal of preventing additional loss of the inner salt marsh complexes, and increasing their size:
Priority recommendation: Fill degraded low-lying areas of marshes with sediment to help restore their historic footprint, and monitor results. In 2003, NPS used a small hydraulic dredge mounted on an open boat to spray a slurry of sediment and bay water taken from a trench in an adjacent tidal creek on to the surface of Big Egg Marsh. The restoration has been “technically successful…as
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the [sprayed] sand is transforming into a silty and organic saltmarsh soil.”100 Assuming results continue to be positive, this technique of “spot filling” through jet or slurry spray should be used to fill in additional low-lying areas of Big Egg Marsh, and sections of Little Egg, Yellow Bar, Goose Pond, Black Bank, Silver Hole, and JoCo Marshes. Spot filling activities should be monitored using an adaptive management strategy, including for purposes of informing future restoration efforts in the bay and elsewhere.
Priority recommendation: Remove artificial
barriers and obstructions to tidal flushing within Jamaica Bay. For example, repairing the drainage culverts located under the Federal Aviation Administration roads to the east of the Rockaway Turnpike and reinstalling the culvert under New York Metropolitan Transportation Authority’s “A” line at 5th Road in Broad Channel would improve the area’s tidal flushing.101
Examine various technologies for non-hardened
structure stabilization to protect the windward side of marsh islands from natural wind and water erosion. Erosion armor of sand-filled bio-degradable tubes or other geo-textiles made of natural or biodegradable fiber could reduce wave erosion and perhaps reduce marsh loss.102
Ensure that the U.S. Army Corps of Engineers’
(Corps’) larger-scale marsh restoration projects, such as those on Elders Point and Yellow Bar, are on schedule and properly funded. The Corps is currently undertaking a restoration project in a portion of Elders Point, with construction and planting scheduled for spring and summer 2006. The plan calls for the Corps to place 315,000 cubic yards of sand on the marsh islands and to construct 61 acres of low-lying marsh. Presently, there are nine acres of marshland on Elders Point.103 The Corps has scheduled Yellow Bar construction and planting for winter 2006 through spring 2007. The Corps will place 80,000 cubic yards of sand on Yellow Bar and will construct 31 acres of low-lying marsh to supplement the existing 77.5 acres of marshland.104
Using lessons learned from the Elders Point and
Yellow Bar restorations, fund and conduct feasibility studies for restoration of Black Wall, Rulers Bar, Duck Point, and Stony Point Marshes. These sites have been severely impacted by marsh loss, and would benefit from additional sediment.
Moreover, sediment could easily be moved on to these locations and monitored by community groups. Feasibility studies are needed before restoration efforts can be begun however, and should be undertaken for these sites as soon as possible.105
Require significantly higher mitigation ratios
(amount of land mitigated in exchange for losing land to development) for tidal wetlands impacts in Jamaica Bay than those required thus far. Throughout the Hudson-Raritan Estuary, the Corps and DEC have typically required mitigation ratios of 2:1 to 3:1 for projects with unavoidable impacts to tidal wetlands and adjacent areas.106 Given the bay’s historic wetland loss, mitigation for unavoidable tidal wetlands impacts in Jamaica Bay should use a 5:1 ratio as a minimum, with higher ratios required as appropriate.
Examine the list of brownfields within the Jamaica
Bay watershed/sewershed and evaluate on a case-by-case basis how to improve their ecological functioning. Remediation and reuse of sites where toxics continue to leach into groundwater could improve conditions in the bay; however, some sites in which natural resources have reemerged may be better left undeveloped. Incentives to help enhance these areas, such as called for in the “Brownfields to Greenfields” program proposed by NY/NJ Baykeeper, should be instituted.107
Pursue alternate sources of marshland restoration
funding, including from private foundations, such as the National Fish and Wildlife Foundation, and from alternative government sources, such as the Environmental Benefits Fund to be created by DEP under the January 2006 Consent Decree with DEC.
Develop a graduated real estate property transfer
tax for new development within the Jamaica Bay watershed to fund marsh restoration. This impact fee could be modeled on an existing program that the East End of Long Island operates by which a portion of the real estate tax helps mitigate the ecological damage of open space loss. Alternatively, a portion of the city’s sales tax could be dedicated to marsh restoration in Jamaica Bay.
Secure funding for New York/New Jersey Harbor
Estuary Program (HEP) priority habitat acquisition and restoration sites located in Jamaica Bay. HEP is part of U.S. Environmental Protection Agency’s
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National Estuary Program and is a stakeholder partnership that works to “develop and implement a plan to protect, conserve, and restore the estuary.”108 One of HEP’s priorities is to acquire, restore, and protect habitat throughout the harbor estuary. HEP’s habitat workgroup is charged with identifying priority acquisition and restoration sites; as of February 2006, HEP has designated 26 sites in Jamaica Bay as priority acquisition and restoration sites.109 It is also important that the involved agencies ensure that designated sites are not developed prior to the opportunity for acquisition.
If filling of borrow pits in Norton Basin and Little
Bay moves forward, use subsequent monitoring data to examine the potential benefits and drawbacks that such recontouring actions might have for the bay’s remaining borrow pits.‡
Initiate long-term planning related to the Belt
Parkway’s renovation and reconstruction that assesses use of design and construction elements that will decrease the highway’s footprint around the rim of Jamaica Bay, increase wetlands and hydrologic connectivity and decrease pollution inputs into the bay.
Goal: Prevent the introduction or spread of
ecologically harmful invasive plant and animal species in and around Jamaica Bay, and reduce their current distribution and population levels as appropriate to improve natural diversity and ecological functions of the Bay.
Goal: Ensure a diverse and healthy population of
native flora and fauna in Jamaica Bay. Recommendations to meet the goals of preventing and reducing invasive species, and ensuring diverse and healthy populations of native flora and fauna:
Priority recommendation: Develop a plan to monitor the spread of invasive species, assess impact on Jamaica Bay’s health, and develop
‡ One committee member dissents from this view, stating that, at this time, he is against the filling of any borrow pits in Jamaica Bay unless it can be scientifically proven that there will be no harmful/detrimental effects to the surrounding area or the bay as a whole. He states that any potential benefits from the filling of Little Bay or Norton Bay should not necessarily be used to initiate action for other areas of the bay due to these areas’ unique differences.
programs for control. For example, Asian shore crabs were recently discovered in areas throughout the bay and more information on the potential impacts these crabs have on green and black-fingered mud crabs is needed, as well as how to eliminate or control their presence in the bay as necessary.110 NPS staff is currently developing a draft invasive plant management plan (to be released in 2007) that identifies target species and areas, and recommends management approaches.
Widely publicize lists of invasive plant and animal
species in Jamaica Bay and set up a hotline or Web site for local residents to notify officials about new invasive species.
Incorporate invasive species control into
restoration projects that target marshes along the bay’s periphery. By returning areas to natural elevations, invasive species, such as Phragmites, will be reduced and the recovered area will be more likely to repopulate with native species.
Restore eelgrass beds in appropriate locations
within the bay, possibly the south side of Little Egg Marsh. Eelgrass beds, which are found in estuarine waters less than eight feet deep, serve as important nurseries and habitats for fishes and shellfishes, help absorb wave action, and improve nutrient uptake and cycling.111 Once found throughout the bay, these beds died off from disease and have been prevented from returning due to degraded water quality and dredging and deepening of former habitat.112 Little Egg Marsh may be an appropriate area for a pilot project because the area is clear of boat traffic and it receives ocean water through the Rockaway Inlet, which are beneficial conditions for eelgrass establishment.
Design and implement community planting
programs using native species. Develop educational materials and a protocol to standardize Jamaica Bay restoration efforts to make them more efficient. The New York City Parks Department serves as a good example as it has implemented similar projects, most notably the Forever Wild Program.113
CHALLENGE: INADEQUATE PLANNING & OUTREACH
The challenges facing Jamaica Bay and its future
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cannot continue to be responded to on an ad hoc basis. More than twenty-five governmental agencies have jurisdictional responsibilities in Jamaica Bay and while they often confer on specific projects, their overall programs lack coordination.114 Differing missions and mandates continue to frustrate the development of an overall plan or vision for Jamaica Bay. 115
Jamaica Bay also lacks an overarching research plan to help guide water quality and habitat restoration studies. Several useful scientific forums have been held, but without a funded, dedicated coordinating structure, scientists have largely approached Jamaica Bay in an individualistic fashion, as targeted grants and specific research interests dictate.
Construction and development within the Jamaica Bay watershed has been conducted without consideration of potential adverse impacts on the bay and sometimes without notice to all interested and affected parties. Enforcement against polluters and clean-ups have not consistently been as strong as needed to preserve the bay’s visual appearance and its ecological integrity.
Finally, and most significantly, Jamaica Bay suffers from a lack of identity outside of a committed core of advocates and users. Jamaica Bay’s beauty and opportunities are largely unknown to the New York City’s residents as a whole. Limited and poor quality access to the bay has prevented even local residents from enjoying this resource and from advocating for its protection and restoration. A much greater political constituency for Jamaica Bay must be created. Otherwise, it will be difficult, if not impossible, to attract necessary public funding and to ensure that government decisionmakers consistently consider the bay’s protection to be a priority. PLANNING AND OUTREACH GOALS & NEXT STEPS
Summary of Planning and Outreach Recommendations
Both increased awareness and use of Jamaica Bay
will foster stewardship of the resource. Integrating a unit about the bay into the school curriculum would add to the number of teachers and students already taking advantage of Jamaica Bay’s natural classroom. Developing additional access points and maps with information on the bay’s offerings would help raise public understanding and foster stewardship of the bay.
The Mayor’s Office of Environmental Coordination should ensure all agencies are notified of upcoming construction and restoration activities, and a
Jamaica Bay-specific environmental assessment form should be created. Restrictions on development and sanctions against illegal activities should be strengthened.
Establishing close ties within the scientific community would avoid duplicative research, allow more effective coordination in a climate of scarce resources and help continually improve understanding and success so critical to moving forward. A conference on restoration and research activities pertinent to Jamaica Bay should be held with the scientific community every two years. A Web site for data sharing among scientists, as well as the larger Jamaica Bay community, should be a priority. Further monitoring stations and studies are needed in order to improve community understanding of the resources.
Specific Planning and Outreach Goals & Recommendations Goal: Institute an ongoing Jamaica Bay
monitoring/science research program that identifies additional scientific needs, and coordinates interagency research and monitoring.
Recommendations to meet the goal of instituting an ongoing Jamaica Bay monitoring/science research program:
Priority recommendation: Increase the number of remote real time monitoring stations in Jamaica Bay and the infrastructure necessary to support these. Current technology allows for marine water quality stations (buoys) to transmit real time data to DEP offices. Routine water quality parameters that should be monitored include salinity, dissolved oxygen, pH, temperature, and nitrogen levels. The selection of station locations should allow for a broad assessment of the bay’s water quality at any point in time. Increased monitoring data will reduce the city’s reliance on analytical modeling and provide a more accurate picture of the ecological system.
New York City, acting through its various agencies
and academic institutions, should facilitate a scientific symposium at least every two years to coordinate and guide scientific investigations on issues pertinent to the ecology of Jamaica Bay and to inform the greater public on the status of the bay’s ecology. Scientific symposiums, such as the Jamaica Bay Institute’s March 2004 “Jamaica Bay’s Disappearing Marshes,” help to not only
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coordinate and guide scientific work, but also to inform the larger public and encourage increased policy action and funding. The city should provide a Web site for the Jamaica Bay community that is regularly updated, coordinated with other relevant Web sites, and made as user-friendly as possible to encourage community groups to interact and network. The Jamaica Bay Research and Management Information Network Web site could fill this need.
Goal: Improve public awareness of and access to
Jamaica Bay. Develop education and outreach programs to
increase knowledge of Jamaica Bay, including the benefits it provides the public, in adjacent communities and in the city as a whole.
Increase the number of public access points to Jamaica Bay.
Increase awareness of Jamaica Bay and its public benefits among elected officials.
Recommendations to meet the goal of improving awareness of and access to Jamaica Bay:
Priority recommendation: Direct the Mayor’s Office of Environmental Coordination to ensure that all relevant state, municipal and federal agencies are notified of construction and restoration activities and their impacts within the Jamaica Bay watershed/sewershed. Create a new Jamaica Bay watershed/sewershed environmental assessment form that ensures additional scrutiny of projects within the Jamaica Bay watershed, with an emphasis on environmental issues pertinent to the bay. The assessment should incorporate an analysis of cumulative impacts, including from related projects; after all, it has been the cumulative effects of countless projects, large and small, over the past 100 years that have so degraded Jamaica Bay. The committee also specifically notes that as the redevelopment of Rockaway Beach and other bay areas continues, standards and requirements must be developed to ensure that such development is fully compatible with the goal of protecting and restoring the bay.
Priority recommendation: Add access points in
Southwestern and Southeastern Queens. There is currently no access of any kind to Jamaica Bay from Southeastern Queens. Crumbling bulkheads, abandoned street ends, and vacant lands cut off communities that lie along the northern shore of the Rockaways and near JFK from the bay. The New York Waterfront Blueprint identified public
access opportunities in this area that would provide a natural link for Brooklyn and Queens residents to each other and to the bay; these should be considered.116
Priority recommendation: Incorporate a unit on the
Jamaica Bay watershed into city science and social studies curricula. Create a program about water and debris entering street catch basins and/or designate one week per year as “Jamaica Bay Conservation Week,” during which students would write essays about the bay.
Develop and distribute a detailed map displaying
access points, boat ramps, parking areas, and walking/biking paths. This map should also include guidelines for how to both enjoy and take care of the resource.
Develop a local nomination process that will allow
the public, according to certain criteria, to nominate additional sites for access and consideration for protection and acquisition.
Require the New York City Department of Health
and Mental Hygiene to conduct a public health survey of people who regularly eat fish from Jamaica Bay and, based on this report, review existing fishing policies. Based on anecdotal information, a significant number of subsistence anglers and their families eat fish from the bay despite New York State Department of Health advisories; the possibility for additional outreach specific to Jamaica Bay should be explored.117
Strengthen enforcement activities and sanctions
against illegal dumping into Jamaica Bay. Businesses with records of polluting behaviors should face additional requirements, such as performance bonds or letters of credit in favor of city permit issuing agencies (DEP, New York City Department of Buildings) when undertaking work within the Jamaica Bay watershed.
Produce an economic analysis of the benefits that
Jamaica Bay’s wetlands provide to the area as a way of encouraging community and business support for investment in the resource.
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1 Hudson River Foundation. 2004. Health of the Harbor: The First Comprehensive Look at the State of the NY/NJ Harbor
Estuary. Prepared for the NY/NJ Harbor Estuary Program. 2 New York City Department of Environmental Protection. 2003. The 2002 New York Harbor Water Quality Report.
New York City Department of Environmental Protection. 2002. The 2001 New York Harbor Water Quality Report. 3 City of New York Local Law 71. 2005. Developing a watershed protection plan for the watershed/sewershed of Jamaica Bay. 4 U.S. Fish and Wildlife Service. No date. Significant habitats and habitat complexes of the New York bight watershed.
Accessed 15 June 2006 from http://training.fws.gov/library/pubs5/web_link/text/jb_form.htm. Audubon New York. No date. Jamaica Bay complex important bird area. Accessed 15 June 2006 from http://ny.audubon.org/iba/jamaicabay.html.
5 City of New York Local Law 71. 2005. Developing a watershed protection plan for the watershed/sewershed of Jamaica Bay. 6 National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004. The Evolving Legacy of Jamaica
Bay. 7 U.S. Army Corps of Engineers-New York District. No date. Jamaica Bay Marsh Islands, NY. Ecosystem restoration study fact
sheet. 8 Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. Recreation vs. waste disposal: The use and management of Jamaica
Bay. Long Island Historical Journal, 5(1), 21-41. 9 Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. 10 National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004.
U.S. National Park Service. No date. Interactive map center. Accessed 24 June 2006 from http://maps.nps.gov/. U.S. Fish and Wildlife Service. 2003. National wildlife refuge system: A visitor’s guide. Accessed 24 June 2006 from
http://www.fws.gov/refuges/pdfs/NWRS_VisitorsGuide_2003.pdf. 11 Davis, T. H. 2002. Birds of Jamaica Bay. Pamphlet revised 2002 by D. Taft; Gateway National Recreation Area. Accessed 19
June 2006 from http://www.nps.gov/gate/jbu/pdf_files/nature_birds_of_jamaica_bay_brochure.pdf. Audubon New York. No date.
12 U.S. Army Corps of Engineers-New York District. 2004, June. Hudson-Raritan Estuary Environmental Feasibility Study: Jamaica Bay Study Area Report. National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004.
13 Karpati, A., X. Lu, F. Mostashari, L. Thorpe, and T.R. Frieden. 2003. The Health of Canarsie and Flatlands. NYC community health profiles; New York City Department of Health and Mental Hygiene, 1(31):1-12. Karpati, A., X. Lu, F. Mostashari, L. Thorpe, and T.R. Frieden. 2003a. The Health of Southwest Queens. NYC community health profiles; New York City Department of Health and Mental Hygiene, 1(30):1-12. Karpati, A., X. Lu, F. Mostashari, L. Thorpe, and T.R. Frieden. 2003b. The Health of the Rockaways. NYC community health profiles; New York City Department of Health and Mental Hygiene, 1(22):1-12.
14 National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004. 15 Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. 16 Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. 17 Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. 18 New York City Department of Environmental Protection. 2004. The 2003 New York Harbor Water Quality Report.
New York City Department of Environmental Protection. 2005. Unpublished 2004 harbor water quality data. Provided by J. Stein.
Hudson River Foundation. 2004. U.S. Army Corps of Engineers-New York District. 2005, June. Norton Basin/Little Bay Technical Summary Report: 2000-2003 Baseline Surveys. Prepared by Barry Vittor & Associates, Lake Katrine, NY.
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20 New York City Department of Environmental Protection. 2003. 21 Swanson, R.L. and R. L. Zimmer. 1990. Meteorological conditions leading to the 1987 and 1988 washup for floatable wastes
on New York and New Jersey beaches and comparison of these conditions with the historical record. Estuarine, Coastal and Shelf Science, 30, 59-78.
22 Potts, M. 2004, December 5. A Shell of the Former Industry. Newsday, G07. Schriebman, M. P. 2006, May 15. Jamaica Bay Watershed Protection Plan. Presentation to the Jamaica Bay Advisory Committee. Wilson, R.E. 2006, 15 May. Present and historic hydrodynamics and sediment dynamics of Jamaica Bay, NY. Presentation to the Jamaica Bay Advisory Committee.
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24 Mankiewicz, P.S. 2005, March 30. 25 New York City Department of Environmental Protection. 2004.
18
Sambrotto, R. No date. Nitrogenous nutrients and plankton production in Jamaica Bay, NY. In Integrated Reconnaissance of the Physical and Biogeochemical Characteristics of Jamaica Bay. Gateway National Recreational Area and Columbia Earth Institute.
26 Kolker, A. 2006, April 26. Salt marsh loss in Jamaica Bay and its relationship to vertical accretion, human impacts and sediment chemistry. Presentation to the Jamaica Bay Advisory Committee.
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Impaired Waters Requiring a TMDL. Accessed 22 June 2006 from http://www.dec.state.ny.us/website/dow/303dcalm.html. 29 Litton, S. 2003, August. Contaminant Assessment and Reduction Project (CARP). New York State Department of
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Program. Accessed 22 June 2006 from www.nyc.gov/html/dep/html/float.html. American Littoral Society-Northeast Chapter. No date. Beach Cleanup News. Accessed 22 June 2006 from www.alsnyc.org.
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Sewer Overflows. Natural Resources Defense Council. Burkhardt, P. 2006, April 27. ‘Green’ roof unveiled by U.S. architect group showcases global trend. Associated Press.
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64 Litton, S. 2003. 65 De Cerreno, A.L.C., M. Panero, and S. Boehme (Eds.). 2002, June. Pollution Prevention and Management Strategies for
Mercury in the NY/NJ Harbor. New York Academy of Sciences. 66 New York City Department of Environmental Protection. 2001, May 7. Use and standards attainment project preliminary
waterbody/watershed characterization report: Paerdegat Basin. 67 Bertrand, D. 2005, July 2005. In the ‘belly’ of the beast: Solar-driven trash cans tested. New York Daily News, 3. 68 Partnerships for Parks. 2000-2005. Outreach and constituency building. Accessed 27 June 2006.
http://www.partnershipsforparks.org/wedo/outreach_constituency.html. 69 New York State Assembly. 2005, January 26. A. 2517-D. Accessed 23 June 2006 from http://assembly.state.ny.us/leg/?bn=
A02517. 70 New York Public Interest Research Group. No date. A bigger, better bottle bill. Accessed 23 June 2006 from
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district. Accessed 23 June 2006 from www.dec.state.ny.us/website/dfwmr/marine/twloss.html. 73 Hudson River Foundation. 2004. 74 National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004.
Hartig, E.K., D. Fallon, F. Mushacke, and A. Kolker. 2001. Wetlands. In Rosenzweig, C. and W.D. Solecki (Eds.). Climate Change and a Global City: The Potential Consequences of Climate Variability and Change—Metro East Coast. Report for the U.S. Global Change Research Program, National Assessment of the Potential Consequences of Climate Variability and Change for the United States, Columbia Earth Institute, New York. 224.
75 National Park Service, Gateway National Recreation Area, and Jamaica Bay Institute. 2004. 76 Hartig, E.K., A. Kolker, and V. Gornitz. No date. Investigations into recent salt marsh losses in Jamaica Bay, New York. In
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20
77 Hartig, E.K., A. Kolker, and V. Gornitz. No date.
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78 U.S. Environmental Protection Agency, National Estuaries Program. 2001, October. Where did all the grass go? Sudden marsh loss in Jamaica Bay, New York. Coastlines, 11.5. Accessed 23 June 2006 from http://www.epa.gov/owow/estuaries/coastlines/oct01/grass.html. U.S. Army Corps of Engineers-New York District. 2004, June.
79 Jamaica Bay Environmental Study Work Group, National Research Council, and Environmental Studies Board. 1971. Jamaica Bay and Kennedy Airport: A Multi-disciplinary Environmental Study. Vol. II. Washington, D.C.: National Academy of Sciences.
80 Houghton R., A. Gordon, and B. Huber. 2000. Dye tracer experiments in Jamaica Bay. In Integrated Reconnaissance of the Physical and Biogeochemical Characteristics of Jamaica Bay. Gateway National Recreational Area and Columbia Earth Institute.
81 Kolker, A. 2006, April 26. Hartig, E.K., A. Kolker, and V. Gornitz. No date.
82 The Trust for Public Land and New York City Audubon Society. 1987. Buffer the Bay: An Updated Report on Jamaica Bay’s Open Shoreline and Uplands.
83 Frame, G. 2005, June 22. Marsh loss and restoration in Jamaica Bay. Presentation to NYWEA MET Chapter Environmental Science Committee Meeting at New York City Department of Environmental Protection, New York.
Frame, G.W., M.K. Mellander, and D.A. Adamo. 2006. Big Egg marsh restoration in Jamaica Bay, New York. In People, Places, and Parks: Proceedings of the 2005 George Wright Society Conference on Parks, Protected Areas, and Cultural Sites. D. Harmon (Ed.). Hancock, Michigan: The George Wright Society.
84 Franz, D.R. and I. Friedman. 2004. Erosion and pool formation in a Jamaica Bay fringing marsh-the mussel berm hypothesis. In Jamaica Bay’s Disappearing Marshes. National Park Service, Gateway National Recreation Area.
85 Frame, G. W., M.D. Byer, M.P. Schreibman, W.S. Panagakos, M.K. Waaijer, and M.K. Mellander. 2004. Effects of wrack (straw & sea lettuce mats) on Smooth Cordgrass Spartina alterniflora survival and recovery in Jamaica Bay Wildlife Refuge, New York: A progress report. In Jamaica Bay’s Disappearing Marshes. National Park Service, Gateway National Recreation Area.
86 Hartig, E.K., A. Kolker, and V. Gornitz. No date. 87 Hartig, E.K., A. Kolker, and V. Gornitz. No date. 88 Hartig, E.K., D. Fallon, F. Mushacke, and A. Kolker. 2001.
Hartig, E.K., V. Gornitz, A. Kolker, F. Mushacke, and D Fallon. 2002, March. Anthropogenic and climate-change impacts on salt marshes of Jamaica Bay, New York City. Wetlands, 22(1).
89 Anonymous. 2002, April 4. Columbia study shows wetlands disappearing near Kennedy Airport. Earth Institute News. Accessed on 23 June 2006 from www.earth.columbia.edu/news/story04_04_02.html. Hartig, E.K., D. Fallon, F. Mushacke, and A. Kolker. 2001.
90 Hartig, E.K., D. Fallon, F. Mushacke, and A. Kolker. 2001. U.S. Fish and Wildlife Service. No date. Anonymous. 2003, September 5. 20 acres of wetland to be restored along Gerritsen Creek. Press Release from U.S. Representative Anthony D. Weiner. Accessed 26 June 2006 from http://www.house.gov/list/press/ny09_weiner/090503wetland.html.
91 Trust for Public Land and New York City Audubon Society. 1987. U.S. Army Corps of Engineers-New York District. 2004, June.
92 U.S. Fish and Wildlife Service. No date. 93 The Trust for Public Land and New York City Audubon Society. 1987. 94 City of New York Local Law 83. 2005. To create a temporary task force to study the feasibility of transferring city-owned
wetlands to the jurisdiction of the department of parks and recreation. 95 New York State Tidal Wetlands Act. 6 NYCRR Part 661. 96 Wenger, S. 1999. A review of the scientific literature on riparian buffer, width, extent, and vegetation. Office of Public
Service & Outreach. Athens, Georgia: Institute of Ecology, University of Georgia. 97 Bredin, J. 2000, April 18. Transfer of development rights: Cases, statutes, examples, and a model. Chicago, IL: 2000 APA
National Planning Conference. Accessed 26 June 2006 from http://www.asu.edu/caed/proceedings00/BREDIN/bredin.htm. 98 Bredin, J. 2000, April 18. 99 New York City Department of Planning. 2002. The new waterfront revitalization plan. Accessed 26 June 2006 from
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21
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Mundy, D. No date. Memo to M. Koenings, L. Houston, K. Chytelo, and P. Heckler, Re: Loss marsh in Jamaica Bay. Jamaica Bay Eco Watchers. 2001, July 26. The second Jamaica Bay Eco Watchers panel & discussion of marsh loss in Jamaica Bay minutes.
106 Harbor Estuary Program Habitat Workgroup. 2001, February 7. Minutes from January 24, 2001 HEP habitat workgroup meeting. Peterson, I. 1989, December 31. Compensating for filling in a wetland. The New York Times, section 10, p. 1. Zeppie. C. 2006, June 26. Personal communication.
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from http://www.seagrant.sunysb.edu/hep/about.htm. 109 New York/New Jersey Harbor Estuary Program Habitat Work Group. 2006, 6 February. Priority acquisition and restoration
sites. Accessed 26 June 2006 from http://www.seagrant.sunysb.edu/hep/restmaps/HabitatSiteList.pdf. 110 Haley, J. Statement at the Brooklyn public hearing on the Jamaica Bay Watershed Protection Plan. 2006, January 11. 111 Prado, M. 13 December 2004. Improved Water Quality Helps Comeback of Bay Eelgrass. The Argus. MIT Sea Grant College Program. 2006. Balance between humans and nature: Eelgrass; What is eelgrass? Massachusetts
Institute of Technology. Accessed 26 June 2006 from http://seagrantdev.mit.edu/eelgrass/eelgrassscience/intro.html. 112 Swanson, R.L. 2006, June 7. Personal Communication.
Swanson, R.L., A.S. West-Valle, and C.J. Decker. 1992. 113 New York City Department of Parks and Recreation. No date. Forever wild: Nature in New York City. Accessed 26 June
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and Recreation, Re: Intro. 565, 566, and Res. No. 830. 117 Lee, D. 2002, July 21. Neighborhood report: New York up close; Don’t drink the water, (and don’t eat the fish). The New
York Times, section 14, p. 5.
Appendix A
LOCAL LAWS
OF
THE CITY OF NEW YORKFOR THE YEAR 2005
No. 71
Introduced by Council Members Gennaro, Avella, Barron, Brewer, Clarke, Comrie, Fidler, Gonzalez, Jennings, Koppell, Liu, Nelson, Palma, Quinn, Recchia, Sanders, Vallone Jr. and Weprin.
A LOCAL LAW
To amend the administrative code of the city of New York, in relation to developing
a watershed protection plan for the watershed/sewershed of Jamaica Bay.
Be it enacted by the Council as follows:
Section 1. Legislative findings and intent. In October of 1972, the United States Congress established the Gateway National Recreation Area (“Gateway”) as part of an effort to bring the National Park System and its ethic of preserving and protecting outstanding resources closer to major urban areas.
Gateway encompasses the largest collection of natural systems, wildlife habitats, historic resources, and recreational opportunities in the New York City/New Jersey metropolitan area. It also encompasses numerous sites of critical natural and cultural importance to the health of local ecosystems, to the life of migratory and native species and to the military, navigational and aviation history of the region and the nation, especially in the context of attendant defenses of New York Harbor.
According to the National Park Service (NPS), Gateway is the only extensive public natural area in the New York City region. The Jamaica Bay Unit is one of several units, consisting of lands, waters, marshes and submerged lands, comprising Gateway. The Jamaica Bay Wildlife Refuge (“Refuge”), established by the City of New York in 1948, is located within the Jamaica Bay Unit. The Refuge, a State and nationally recognized important bird area, encompasses 2,500 acres within the boroughs of Brooklyn and Queens. The only wildlife refuge in the National Park System, it provides a shelter for rare and endangered birds and a variety of habitats for more than 325 kinds of waterfront and shorebirds. It is also a critical stop-over area along the Eastern Flyway migration route and is one of the best and world renowned bird-watching locations in the western hemisphere.
Jamaica Bay is one of the largest and most productive coastal ecosystems in the State of New York, as well as within the Northeastern United States, and is an important recreational destination for local, national and international visitors. It contains approximately 13,000 acres of surface waters, including the largest tidal wetland
2 complex in New York State. These wetlands provide benefits such as natural water quality improvement, flood protection and shoreline erosion control for the commercial and residential areas in and around the Bay in Brooklyn and Queens. Unfortunately, construction and development within the Jamaica Bay watershed has often been conducted without consideration of potential adverse impacts on the Bay and sometimes without notice to all interested governmental agencies, civic groups and other interested parties. One such governmental agency is the NPS, which is the primary steward of the Bay, itself, and with whom, among many other agencies, it is critical for the City to collaborate in order to protect the Bay.
Jamaica Bay’s future as an oasis of great ecological importance is in severe jeopardy due to the fact that thousands of acres of the Bay’s marshy islands, which serve as nesting and feeding areas for an abundance of birds and other wildlife, are rapidly and mysteriously vanishing. Scientists predict that the Jamaica Bay marshlands will completely vanish in less than twenty years if the cause of their deterioration and a solution to their preservation are not found.
This legislation would require the New York City Department of Environmental Protection to create a watershed protection plan for the watershed/sewershed of Jamaica Bay, and would create a Jamaica Bay watershed protection plan advisory committee. The Council finds that such watershed planning is vital to the future of Jamaica Bay. This legislation establishes the initial pathway towards restoring and maintaining the water quality and ecological integrity of the Bay by comprehensively assessing threats to the Bay and coordinating environmental remediation and protection efforts in a focused and cost-effective manner. Watershed protection planning for Jamaica Bay is an efficient and effective means of promoting the sustainability of the Bay’s environment, the economy associated with the Bay, and the linkages between the two.
§2. Chapter five of title 24 of the administrative code of the city of New York is hereby amended by adding thereto a new section 24-527 to read as follows:
§24-527 Watershed protection plan for the watershed/sewershed of Jamaica bay. a. No later than September 1, 2006, the commissioner shall complete a watershed protection plan for the watershed/sewershed of Jamaica bay, which shall, among other things, include measures the city can implement to help protect Jamaica bay. The overall goal of such plan shall be to restore and maintain the water quality and ecological integrity of Jamaica bay.
b. The commissioner shall assess the technical, legal, environmental and economical feasibility of including the following measures, at minimum, in the plan prepared pursuant to subdivision a of this section:
(1) best management practices for the minimization and control of soil erosion and stormwater runoff and reduction of both point and non-point source pollution, including, but not limited to, the promotion of development practices such as the on-site detention and infiltration of stormwater runoff, the minimization of impervious surfaces and the creation of natural systems to control and minimize stormwater runoff;
(2) measures to address threats to aquatic habitat, including, but not limited to, stabilizing and restoring salt marshes, wetlands, soils and other natural areas, strengthening ecological buffers, restoring natural features to the Jamaica bay watershed/sewershed shoreline, and reestablishing water flows;
(3) land acquisition and land use planning practices and opportunities, including, but not limited to, incentives, such as expedited permitting and property tax relief, for infill, brownfield redevelopment and other environmentally beneficial development, and
3 disincentives, such as stricter development guidelines, for development that may adversely impact Jamaica bay;
(4) a protocol for coordination with appropriate federal, state and city governmental entities that have jurisdiction over the Jamaica bay area, with respect to, but not limited to, efforts to restore and maintain the water quality and ecological integrity of Jamaica bay and notification regarding proposed development projects within the Jamaica bay watershed/sewershed that may adversely impact Jamaica bay;
(5) a protocol for coordination with the office of environmental coordination that ensures that environmental assessments and reviews of projects within the Jamaica bay watershed/sewershed address potential impacts to Jamaica bay and are conducted pursuant to all applicable federal, state and city environmental quality review laws and regulations;
(6) a public education program, including, but not limited to, programs for schools, developers, commercial facilities, civic groups and other local organizations and entities to increase awareness about the ecological significance and degradation of Jamaica bay; potential threats to Jamaica bay; restoration and watershed stewardship activities undertaken by the department and others involving Jamaica bay; and methods and practices to reduce pollution in Jamaica bay; and
(7) a program to target enforcement efforts that will help reduce polluting behaviors and operations that may adversely impact Jamaica bay.
c. The watershed protection plan prepared pursuant to subdivision a of this section, as it may be revised pursuant to subdivision f of this section, shall contain the following:
(1) specific goals related to restoring and maintaining the water quality and ecological integrity of Jamaica bay;
(2) the geographic boundaries of the watershed/sewershed of Jamaica bay for the purpose of achieving the goals of such plan and an explanation for the selection of such boundaries;
(3) the assessments the commissioner completed for each measure considered for inclusion in such plan;
(4) for any final recommendation of the Jamaica bay watershed protection plan advisory committee established pursuant to subdivision h of this section that was not assessed for inclusion or incorporated in such plan, an explanation for such omission; and
(5) a schedule, including interim and final milestones, for implementing the measures and achieving the specific goals included in such plan and methods of monitoring progress towards achieving such milestones and goals.
d. The commissioner shall implement the plan prepared pursuant to subdivision a of this section, as it may from time to time be revised pursuant to subdivision f of this section, in accordance with its provisions.
e. The commissioner shall submit to the mayor and the speaker of the council the watershed protection plan prepared pursuant to subdivision a of this section, or any revised plan prepared pursuant to subdivision f of this section, no later than five business days after its completion.
f. The watershed protection plan prepared pursuant to subdivision a of this section shall be reviewed and revised as necessary to achieve its goals, but in no event shall such review occur less often than once every two years.
g. No later than October 1, 2007, and no later than October 1 every two years thereafter, the commissioner shall submit a report to the mayor and the speaker of the council, which shall include, but not be limited to:
4 (1) the implementation status of the measures included in the watershed protection
plan prepared pursuant to subdivision a of this section, as it may have been revised pursuant to subdivision f of this section; and
(2) where the plan has been reviewed in accordance with subdivision f of this section and the commissioner determines that no revisions are required, such determination and the reasons for it.
h. (1) A Jamaica bay watershed protection plan advisory committee shall be established, which shall provide advice to the commissioner for the duration of its term and provide final recommendations to the commissioner and the speaker of the council on the watershed protection plan prepared pursuant to subdivision a of this section regarding:
i. the specific goals of such plan related to restoring and maintaining the water quality and ecological integrity of Jamaica bay;
ii. the geographic boundaries of the watershed/sewershed of Jamaica bay to be included in such plan;
iii. any measures that should be assessed by the commissioner for inclusion in such plan, in addition to those listed in subdivision b of this section;
iv. the assessment of the technical, legal, environmental and economical feasibility of including in such plan the measures listed in subdivision b of this section and any additional measures; and
v. a schedule, including interim and final milestones, for implementing the measures and achieving the specific goals to be included in such plan and methods of monitoring progress towards achieving such milestones and goals.
(2) Such advisory committee shall be comprised of seven members, three of whom shall be appointed by the speaker of the council and four by the mayor. The members shall be appointed within forty-five days after the effective date of this section and shall serve without compensation. The chairperson shall be elected from amongst the members. Any vacancy shall be filled in the same manner as the original appointment for the remainder of the unexpired term. The commissioner may provide staff to assist the advisory committee.
(3) Such members of the advisory committee shall serve until three months after the date upon which the commissioner completes the watershed protection plan prepared pursuant to subdivision a of this section, after which time the committee shall cease to exist.
(4) No later than July 1, 2006, the chairperson of such committee shall submit a report containing its final recommendations to the commissioner and the speaker of the council.
§3. This local law shall take effect immediately.
5 THE CITY OF NEW YORK, OFFICE OF THE CITY CLERK, s.s.:
I hereby certify that the foregoing is a true copy of a local law of the City of New York, passed by the Council on June 30, 2005, and approved by the Mayor on July 20, 2005.
VICTOR L. ROBLES, City Clerk of the Council
CERTIFICATION PURSUANT TO MUNICIPAL HOME RULE LAW §27 Pursuant to the provisions of Municipal Home Rule Law §27, I hereby certify that
the enclosed Local Law (Local Law 71 of 2005, Council Int. No. 565-A) contains the correct text and:
Received the following vote at the meeting of the New York City Council on June 30, 2005: 50 for, 0 against, 0 not voting.
Was signed by the Mayor on July 20, 2005. Was returned to the City Clerk on July 21, 2005.
JEFFREY D. FRIEDLANDER, Acting Corporation Counsel
Appendix B
1
Int. No. 376
By Council Members Gennaro, Addabbo Jr., Brewer, Clarke, Fidler, Gerson, James, Koppell,
Liu, Mark-Viverito, Monserrate, Nelson, Sanders Jr., Sears and Weprin
A Local Law to amend the administrative code of the city of New York, in relation to the
watershed protection plan for the watershed/sewershed of Jamaica Bay.
Be it enacted by the Council as follows:
Section 1. Section 24-527 of the administrative code of the city of New York is amended
to read as follows:
§24-527 Watershed protection plan for the watershed/sewershed of Jamaica bay. a. No
later than September 1, [2006]2007, the commissioner shall complete a watershed protection
plan for the watershed/sewershed of Jamaica bay, which shall, among other things, include
measures the city can implement to help protect Jamaica bay. The overall goal of such plan shall
be to restore and maintain the water quality and ecological integrity of Jamaica bay.
b. The commissioner shall assess the technical, legal, environmental and economical
feasibility of including the following measures, at minimum, in the plan prepared pursuant to
subdivision a of this section:
(1) (1) best management practices for the minimization and control of soil erosion and
stormwater runoff and reduction of both point and non-point source pollution, including, but not
limited to, the promotion of development practices such as the on-site detention and infiltration
of stormwater runoff, the minimization of impervious surfaces and the creation of natural
systems to control and minimize stormwater runoff;
(2) (2) measures to address threats to aquatic habitat, including, but not limited to,
stabilizing
2
and restoring salt marshes, wetlands, soils and other natural areas, strengthening ecological
buffers, restoring natural features to the Jamaica bay watershed/sewershed shoreline, and
reestablishing water flows;
(3) land acquisition and land use planning practices and opportunities, including, but not
limited to, incentives, such as expedited permitting and property tax relief, for infill, brownfield
redevelopment and other environmentally beneficial development, and disincentives, such as
stricter development guidelines, for development that may adversely impact Jamaica bay;
(4) (4) a protocol for coordination with appropriate federal, state and city governmental
entities
that have jurisdiction over the Jamaica bay area, with respect to, but not limited to, efforts to
restore and maintain the water quality and ecological integrity of Jamaica bay and notification
regarding proposed development projects within the Jamaica bay watershed/sewershed that may
adversely impact Jamaica bay;
(5) (5) a protocol for coordination with the office of environmental coordination that
ensures
that environmental assessments and reviews of projects within the Jamaica bay
watershed/sewershed address potential impacts to Jamaica bay and are conducted pursuant to all
applicable federal, state and city environmental quality review laws and regulations;
(6) a public education program, including, but not limited to, programs for schools,
developers, commercial facilities, civic groups and other local organizations and entities to
increase awareness about the ecological significance and degradation of Jamaica bay; potential
threats to Jamaica bay; restoration and watershed stewardship activities undertaken by the
3
department and others involving Jamaica bay; and methods and practices to reduce pollution in
Jamaica bay; and
(7) a program to target enforcement efforts that will help reduce polluting behaviors and
operations that may adversely impact Jamaica bay.
c. The watershed protection plan prepared pursuant to subdivision a of this section, as it
may be revised pursuant to subdivision [f]h of this section, shall contain the following:
(1) (1) specific goals related to restoring and maintaining the water quality and
ecological
integrity of Jamaica bay;
(2) (2) the geographic boundaries of the watershed/sewershed of Jamaica bay for the
purpose
of achieving the goals of such plan and an explanation for the selection of such boundaries;
(3) (3) the assessments the commissioner completed for each measure considered for
inclusion
in such plan;
(4) for any final recommendation of the Jamaica bay watershed protection plan advisory
committee established pursuant to subdivision [h]j of this section that was not assessed for
inclusion or incorporated in such plan, an explanation for such omission; and
(5) a schedule, including interim and final milestones, for implementing the measures and
achieving the specific goals included in such plan and methods of monitoring progress towards
achieving such milestones and goals.
4
d. No later than September 1, 2006, the commissioner shall complete an interim report on
the preparation of the watershed protection plan required pursuant to subdivision a of this
section, which shall include, at minimum, the following elements:
(1) a description of the current status of the plan preparation, including, but not limited to,
the status of all feasibility assessments of measures conducted pursuant to subdivision b of this
section; and
(2) for each preliminary recommendation of the Jamaica bay watershed protection plan
advisory committee provided to the commissioner pursuant to paragraph four of subdivision j of
this section, the commissioner shall state whether:
i. i. the recommendation will be incorporated into the plan required pursuant
to
subdivision a of this section;
ii. ii. the recommendation will not be incorporated into such plan, in which
case the
commissioner shall provide a detailed explanation of the basis for any such omission; or
iii. iii. the recommendation will be further assessed for inclusion in such plan,
in which case
the commissioner shall provide a detailed explanation of the reason for such further assessment,
including a timeline for such assessment’s completion.
e. No later than March 1, 2007, the commissioner shall complete a draft of the watershed
protection plan for the watershed/sewershed of Jamaica bay required pursuant to subdivision a of
this section.
f. The commissioner shall implement the plan prepared pursuant to subdivision a of this
5
section, as it may from time to time be revised pursuant to subdivision [f]h of this section, in
accordance with its provisions.
[e]g. The commissioner shall submit to the mayor and the speaker of the council the
watershed protection plan, draft of such plan and interim report prepared pursuant to
subdivisions a, d and e of this section, or any revised plan prepared pursuant to subdivision [f]h
of this section, no later than five business days after its completion.
[f]h. The watershed protection plan prepared pursuant to subdivision a of this section
shall be reviewed and revised as necessary to achieve its goals, but in no event shall such review
occur less often than once every two years.
[g]i. No later than October 1, [2007]2008, and no later than October 1 of every
[two]second year[s] thereafter, the commissioner shall submit a report to the mayor and the
speaker of the council, which shall include, but not be limited to:
(1) (1) the implementation status of the measures included in the watershed protection
plan
prepared pursuant to subdivision a of this section, as it may have been revised pursuant to
subdivision [f]h of this section; and
(2) where the plan has been reviewed in accordance with subdivision [f]h of this section
and the commissioner determines that no revisions are required, such determination and the
reasons for it.
[h]j. (1) A Jamaica bay watershed protection plan advisory committee shall be
established, which shall provide advice to the commissioner for the duration of its term and
provide preliminary and final recommendations to the commissioner and the speaker of the
6
council on the watershed protection plan prepared pursuant to subdivision a of this section
regarding:
i. the specific goals of such plan related to restoring and maintaining the water quality
and ecological integrity of Jamaica bay;
ii. the geographic boundaries of the watershed/sewershed of Jamaica bay to be included
in
such plan;
iii. any measures that should be assessed by the commissioner for inclusion in such plan,
in addition to those listed in subdivision b of this section;
iv. the assessment of the technical, legal, environmental and economical feasibility of
including in such plan the measures listed in subdivision b of this section and any additional
measures; and
v. a schedule, including interim and final milestones, for implementing the measures and
achieving the specific goals to be included in such plan and methods of monitoring progress
towards achieving such milestones and goals.
(2) Such advisory committee shall be comprised of seven members, three of whom shall
be appointed by the speaker of the council and four by the mayor. The members shall be
appointed within forty-five days after the effective date of this section and shall serve without
compensation. The chairperson(s) shall be elected from amongst the members. Any vacancy
shall be filled in the same manner as the original appointment for the remainder of the unexpired
term. The commissioner may provide staff to assist the advisory committee.
7
(3) Such members of the advisory committee shall serve until three months after the date
upon which the commissioner completes the watershed protection plan prepared pursuant to
subdivision a of this section, after which time the committee shall cease to exist.
(4) No later than July 1, 2006, the chairperson(s) of such committee shall submit a report
containing the committee’s preliminary recommendations regarding the watershed protection
plan prepared pursuant to subdivision a of this section to the commissioner and the speaker of the
council.
(5) No later than [July 1, 2006]June 1, 2007, the chairperson(s) of such committee shall
submit a report containing [its]the committee’s final recommendations regarding the watershed
protection plan prepared pursuant to subdivision a of this section to the commissioner and the
speaker of the council.
§2. This local law shall take effect immediately.
PCW 6/7/06
LS #1173
Appendix C
PENIN
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I 495
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MARCUS AVE
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NGROVEST
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W SUNRISE HWY
N6THST
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STRATFORD AVE6TH AVE
L ST
ROCKAWAYAVE
EMERSONPL
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SCRANTON AVE
PARKLN
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N2NDST
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HILLAVE
G ST
EARLEAVE
UNIONTPKE
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LYONST
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BRYANT
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DENTONAVE
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LANDAUAVE
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SALEMRD
COCHRANPL
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JAMESST
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NAPLE AVE
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DORISAVE
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WELLINGTONRD
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OAKDR
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ROLLINGST
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LAKE DR
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LEIGHTON RD
116TH RD
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4THST
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PINEST
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238THST
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225THST
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CHARLESST
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EDWARDST
VIRGINIADR
PILGRIMST
WOODLAND RD
BLYCT
LESOIRAVE
LOTUSST
PAULPL
BARNES ST
VINE ST
DAVIS ST
SURREY CMNS
ABRAMSPL
RUTGERS RD
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LENNOXCT
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PL
ALVINPL
8THST
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SUNNYLN
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PARKHURST RD
S16THST
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85TH AVE
INIPDR
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W SUNRISE HWY
RAMP
OAK ST
BROADWAY
STEWARTST
I 495
5THAVE
DENTONAVE
AV U
AV JSHOREPY
AV I
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E7ST
PITKIN AV
BEDFORDAV
AV Y
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AV Z
E27ST
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E22ST
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E21ST
E14ST
AVT
E29ST
E13ST
E12ST
E24ST
E18ST
AV S
NOSTRANDAV
CROSSBAYBL
E23ST
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147 AV
E9ST
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AVL
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NONAME
AVK
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JAMAIC
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233ST
AV O
130ST
AV P
120ST114ST
AVN
234ST
AVM
AV R
111ST
118ST
FARMERSBL
116ST
RALPHAV
E53ST
REMSENAV
CONEYISLANDAV
MERRICK BL
AVD
81 AV
E55ST
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FOCH
BL
147ST
E52ST
E17ST
E56ST18
AV
121ST
146ST
SUTPHINBL
102ST
MCDONALDAV
E51ST
FLATLANDSAV
263ST
249ST
135ST
AV X
202ST
90ST
145ST
CHURCH AV
PARK LA
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140ST
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92AV
FULTO
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257ST
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UNION
TP
86ST
ROGERSAV
199ST
258ST
201ST
203ST
E59ST
E80ST
84ST
85ST
115ST
111AV
GLENMORE
AV
259ST
E85ST
157ST
LENOX RD
E86ST
E84ST
80 AV
157 AV
260ST
E19ST
104ST
E49ST
116 AV
160ST
113ST
E57ST
180ST
47ST
112AV
264ST
83ST
261ST
SNYDER AV
52ST
44ST
229ST
232ST
INWOODST
43ST
50ST
E102ST
E93ST
266ST
45ST
226ST
J F K ACCESSRD
267ST
252ST
42ST
E48ST
149 AV
E65ST
230ST
37ST
227ST
231ST
98ST
53ST
CROWN ST
15AV
48ST
144ST
BELMONT A
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251ST
41ST
AVB
E108ST38
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MAPLE ST
250ST
VANWYCKEPSRW
GUYRBREWERBL
168ST
93ST
14AV
40ST
E26ST
E33ST
265ST
207ST
VANSICLENAV
BROOKVILLEBL
E2ST
46ST
49ST
215PL
76ST
39ST
VERMONTST
MILLERAV
217ST
ROCKAWAYAV
216ST
E66ST
STANLEYAV
WILLIAMSAV
E82ST
16AV
144 AV
EMPIRE BL
100ST
248ST
CATON AV
LOGANST
247ST
12AV
VANWYCKEPSRE
GERRITSENAV
E103ST
COZINE AV
BROOKLYNAV
218ST
268ST
91ST
NEWKIRKAV
ROCKAWAYBL
220ST
N CONDUIT AV
NEWLOTSAV
E95ST
124ST
125ST
ATKINSAV
RUGBYRD
200ST
CLARKSON AV
E15ST
CARROLL ST
GLENWOODRD
122ST
214ST
HOOKCREEKBL
E46ST
RUTLAND RD
E63ST
215ST
E64ST
WINTHROPST
CLARENDONRD
E94ST
E81ST
LEIF ERICSO
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AV C
BEACH
CHANNEL DR
E99ST
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CORTELYOU R
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E101ST
213ST
114PL
84DR
LEFFERTS AV
EMMONS AV
ALBANYAV
142ST
E92ST
112ST
160 AV
159 AV
161 AV
JUNIUSST
E38ST
158 AV
E39ST
E40ST
169ST
212PL
105ST
141ST
BAYPY
79 AV
E32ST
RYDERST
SNEDIKERAV
230PL
BLAKE AV
94AV
126ST
E69ST
148 AV
WESTST
E71ST
84 AV
STATERD
175ST
NEWPORT AV
114 AV
122PL
LIBERTYAV
143ST
AVA
93 AV
STUARTST
ARCHER
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LINDEN BL
WYONAST
E16ST
E104ST
SOUTHRD
MILLAV
HEGEMANAV
HOPKINSONAV
DITMASAV
WORTMANAV
103ST
113 AV
E34ST
HILLSIDE
AV
147 RD
148 RD
W3ST
ESSEXST
PARKSIDE AV
99ST
LOUISIANAAV
20AV
224ST
210ST
228ST
E35ST
E91ST
148 DR
130 AV
NASSAU EP
131ST
CROSSISLAND
PY
E96ST
77ST
219ST
246ST
218PL
81ST
ETNA ST
151 AV
112RD
165ST
MONTGOMERY ST
87 DR
140 AV
108ST
84 RD
E74ST
255ST
237ST
MIDWOOD ST
BRISTOLST
168PL
149 RD
60ST
98 AV
KNAPPST
COLEMANST
VOORHIES AV
HENLEYRD
148ST
177ST
LAURELTONPY
164PL
244ST
NORTHSR
TROYAV
E31ST
77AV
150 AV
209ST
SAYRESAV
205ST
BRADDOCK AV
59ST
87RD
87 AV
BAISLEYBL
BEDELLST
99 AV
150ST
VANWYCKEP
18ST
16 ST
FOSTERAV
73AV
191ST
BATCHELDERST
DUMONT
AV
147 DR
DUNKIRKST
BR6ST
20ST
8 AV
19ST
225ST
158ST
E45ST
SPRINGFIELDBL
SOUTHERN
PY
162ST
DAHILLRD
TILDEN AV
163 AV
LINWOODST
162 AV
MILFORDST
ROCKAWAY
FY
S CONDUIT AV
AUTUMNAV
51ST
270ST
MOTTAV
91 AV
CARGOPZ
WESTMINSTERRD
BCH67ST
94RD
243ST
E36ST
MONTAUKAV
97ST
132ST
FLATBUSHAV
STRAUSSST
RIDGEW
OOD AV
PARK PL
AV F
138ST
E78ST
221ST
ROCKAWAYPY
178PL
135PL
SCHENECTADYAV
EASTDR
W4ST
CRONSTON
AV
PENNSYLVANIAAV
114 DR
BRAGGST
170ST
E72 ST
LITTLENECKPY
SHORE PY SR S
156 AV
198ST
SHEPHERDAV
19AV
100 AV
79ST
EUCLIDAV
130PL
242ST
E43ST
21AV
PARSONSBL
195ST
E89ST
E1ST
107 AV
117ST
BR4ST
190ST
NASHVILLEBL9
2ST
102RD
161ST
109AV
LORING AV
205PL
LINCOLN RD
271ST
ELTONST
54ST
UNNAMEDST
238ST
LAKEST
159ST
222ST
E11ST
FTHAMILTON
PY
121 AV
MYRTLE AV
78ST
EASTERNPYEX
HARINGST B
CH20ST
137 AV
223ST
MOTHERGASTONBL
E42ST
189ST
AUSTINST
NEWYORKAV
134ST
253ST
SEAGIRT BL
62ST
SCHENCKAV
154ST
METROPOLITAN AV
92 RD
E37ST
GRANDCENTRALPY
89 AV
178ST
AV W
64ST
E88ST
ALABAMAAV
107ST
217LA
AV H
VANDALIAAV
141 AV
NEPTUN
E AV
CRESCENTST
HIGHLANDBL
FENIMORE ST
QUENTINRD
GRANTAV
75ST
82ST
184PL
143 AV
88ST
E25ST
WESTDR
ROCKAWAY B
EACH BL
187PL
LONGST
211ST
186ST
NASSAU EP ET WB
75 AV
HALEAV
254ST
87ST
HEALY A
V
WEXFO
RDTE
96ST
86 AV
PAERDEGAT AVN
142PL
SUTTER AV
BCH43ST
90AV
PROSPECT
AV
114 RD
BAY25ST
128ST
127 AV
179PL
MARINEPYBR
BCH65ST
116 DR
COLFAX
ST
RANGE R
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88 AV
181ST
179ST
BOARDWALK E
116RD
171PL
E6ST
126 AV
1ST
184ST
CORBINPL
CENTRALAV
DOVERST
FOUNTAINAV
LINCOLNAV
REDFERNAV
183ST
E87ST
88 RD
172ST
DALNYRD
106ST
109ST
115DR
110ST
188ST
ST JOHN'S PL
138 AV
164ST
193ST
PRESTONCT
201PL
142 RD
119AV
135 AV
118AV
BCH63ST
125 AV
SERVICERD
76AV
COYLEST
DARECT
CENTERDR
106 AV
129 AV
111RD
BARBEYST
90 RD
96PL
235ST
CANEYLA
BERGENAV
139 AV
SPRINGFIELDLA
192ST
DICKENSST
PARKVILLEAV
176ST
85 DR
115 RD
105 AV
173ST
BCH45ST
80ST
ATLANTIC AV
138PL
BR11ST
DICTUMCT
MADISONPL
BR1ST
NORTONDR
166ST
BCH22ST
144 DR
152 AV
BAY32ST
AMHERSTST
239ST
115AV
104 AV
146 TE
HOLLIS
COURTBL
167ST
241ST
128AV
PRESIDENT ST
129ST
WEST END AV
86 RD
127ST
155 AV
MAYFAIRDR
S
156ST
CONCHPL
FLOYDBENNETTFIELD
BCH54ST
132AV
VETERANS AV
95ST
133ST
120 AV
94ST
CROSSBAYBR
139ST
CRYSTALST
120 RD
82AV
EASTERN PY
KENO
AV
HIGHLANDPL
UNION ST
208 ST
122 AV
110 RD
149 DR
RUBYST
BURNETTST
DOUGLA
S AV
101ST
WHITMANDR
BCH13ST
236ST
136 AV
145 RD
LOTTST
146 AV
182ST
DUNTONAV
JEROMEST
BAY24ST
ALMEDAAV
ALBEMARLE R
D
194ST
BCH141ST
136ST
169PL
WOODHULLAV
ASHFORDST
IRACT
196ST
72 AV
164 AV
197ST
147PL
85 RD
DE WITT AV
BCH35ST
BUSHWICK
AV
SEAWALLAV
ELDERTLA
BEVERLY RD
123ST
BAYFIELD AV
235CT
204ST
BCH126ST
BCH59ST
BCH38ST
AVV
153AV
95AV
110AV
SCHENCKST
E 9 RD
E61ST
MURRAYRD
E 6 RD
BRISBINST
IRWINPL
4 AV
IRWINST
145 AV
BR13ST
W 18 RD
72RD
GRAVESEND NECK RD
212ST
E58ST
GIRARDST
BCH40ST
SAWYERAV
171ST
SHOREPYENWB
3 ST
133 AV
BAYSIDE DR
AVIATIO
NRD
BCH220ST
85 AV
99PL
SEAVIEWAV
AMSTEL BL
BCH124ST
BCH30ST
E41ST
FARRAGUTRD
97 AV
PALMER DR
HENDRIXST
131 RD
BCH222ST
165 AV
117 RD
E53PL
174ST
E70ST
103 AV
GEORGIAAV
SHERMANST
W 16 RD
KENILWORTHPL
HAWTREEST
101 AV
74PL
134 AV
AMBERST
W 11 RD
E106ST
W 14 RD
BCH9ST
145 DR
LEFFERTSBLS
HEFFIELDAV
PINEST
BCH169ST
BCH56ST
153ST
BCH122ST
BCH193ST
BCH146ST
GAINCT
108AV
COMMISSARYRD
131 AV
REDDINGST
BROADST
DECATURAV
BCH97ST
POINTBREEZEPL
WOODHAVENBL
MADOCAV
BCH61ST
BCH27ST
CHURCHLA
BCH120ST
OXFORDST
BCH144ST
BELKNAPST
LANGHAMST
CHANDLERST
150 DR
BCH148ST
NIXONCT
BANNER AV
DEXTERCT
BCH118ST
71 AV
130 RD
134 RD
146 RD
158ST
118 AV
213ST
96ST
E22ST
120AV
189ST
E53ST
232ST
E56ST
NONAME
88 AV
94AV
164ST
113ST
105AV
221ST
228ST
116AV
SHEPHERDAV
96ST
168ST
119 AV
LINDEN B
L
88 AV
116ST
125ST
224ST
86 RD
NONAME
134 AV
88ST
143ST
NONAME
90ST
95ST
93AV
E32ST
120ST
111AV
AV N
NONAME
E35ST
250ST
86 AV
117ST
118ST
133 AV
E21ST
136 AV
84AV
E86ST
184ST
148 AV
AV O
126ST
161 AV
AVX
NO NAME
150 AV
221ST
162 AV
E46ST
WYONAST
UNIONTP
108ST
114ST
123ST
176ST
BEVERLY RD
91ST
E55ST AV
J
142ST
NO NAME
218ST
AV N
DITMASAV
199ST
AV X
E4ST
123ST
E58ST
E51ST
75ST
113AV
NONAME
116AV
183ST
GLENWOOD R
D
78ST
88ST
80ST
130ST
E49ST
175ST
E58ST
145 RD
137 AV
247ST
150ST
SUTTER AV
118ST
AVM
197ST
109ST
E10ST
S CONDUIT AV
98ST
E17ST
105ST
E38ST
168ST
86 AV
218ST
140 AV
NO NAME
93 AV
E92ST
201ST
79ST
129ST
NONAME
KNAPPST
224ST
81ST
89ST
AV L
E28ST
107ST
NONAME
203ST
E40ST
198ST
E17ST
176ST
AVV
E96ST
76AV
82ST
115AV
NONAME
85ST
93 AV
109 AV
115AV
108 AV
109 AV
ALBEMARLE R
D
95ST
NONAME
E4ST
208ST
127ST
106ST
86ST
108 AV
AV I
241ST
12 AV
78ST
E38ST
CHURCH
AV
85 RD
205ST
249ST
149 AV
119 AV
E2ST
E94ST
178ST
195ST
87 AV
109AV
91 AV
254ST
226ST
E16ST
E46ST
115 RD
121ST
218ST
E34ST
150 AV
89ST
E38ST
NONAME
ELTONST
SUTTER AV
NONAME
84 RD
122ST
E1ST
120 AV
204ST
109 AV
97 AV
96ST
130AV
111 AV
101AV
86 RD
NONAME
80ST
220ST
NONAME
E52ST
118AV
112 AV
NONAME
130 AV
AV M
E32ST
132ST
OCEANAV
E9ST
AV T
E48ST
222ST
159ST
E58ST
E18ST
NO NAME
102ST
110AV
AV O
E48ST
AV H
E40ST
133ST
230ST
92ST
125ST
86ST
104AV
131AV
AVN
135 AV
NONAME
AV H
222ST
86AV
E16ST
232ST
E34ST
207ST
143ST
156 AV
93 AV
232ST
124ST
NONAME
127ST
134 AV
99 AV
111 RD
TROYAV
NO NAME
112ST
134ST
AVP
OCEANPY
E10ST
177ST
123ST
76ST
219ST
115ST
85 AV
E91ST
89AV
131ST
223ST
E58ST
DAHILLRD
115ST
FOSTERAV
NONAME
AV V
196ST
144 AV
78ST
E26ST
88 AV
130PL
E19ST
E49ST
E31ST
NONAME
129 AV
94AV
103AV
89 AV
107AV
E7ST
E34ST
E22ST
NO NAME
SUTTER AV
NO NAME
E34ST
NONAME
E58ST
196ST
E95ST
95 AV
BCH65ST
NONAME
72AV
TROYAV
111 AV
89 AV
E9ST
BERGENAV
E42ST
122 AV
99ST
NONAME
87ST
AV P
AV D
AV K
137 AV
100AV
88ST
115 AV
E87ST
133 AV
AV K
145 AV
86 AV
133 AV
E29ST
219ST
226ST
E2ST
133 AV
183ST
89 AV
NO NAME
-0 1 20.5 Miles
Queens
Brooklyn
Legend
Watershed
nassauwatershed
Centerline
Jamaica Bay Watershed
Jamaica
26 Ward
Coney Island
Rockaway
20% of theWatershedexists inNassau County
3Q
3Q
3Q
3Q
6
9
1011
6
8
5
9
12
5
13
12
-0 1 20.5 Miles
Queens
Brooklyn
Flows toOwls Head
Legend
3Q Water Treatment Plant
Watershed
Sewershed
Congressional District
Queens Congressional Districts
5. Gary Ackerman6. Gregory Meeks8. Jerrold Nadler9. Anthony Weiner
Brooklyn Congressional Districts
10. Edolphus Towns11. Major Owens12. Nydia Velazquez13. Vito Fossella
Jamaica Bay Watershed / Sewershed Congressional Districts
Jamaica
26 Ward
Coney Island
Rockaway
20% of theWatershedexists inNassau County
Appendix D
1
LIST OF COMMITTEE MEMBERS INCLUDING AFFILIATIONS AND BIOGRAPHIES Doug Adamo Since his appointment as Chief of the Division of Natural Resources at Gateway National Recreation Area in March, 2003, Doug Adamo has worked in coordination with National Park Service and Gateway natural resource staff on a variety of issues/efforts focusing on Jamaica Bay resources. The largest effort was the Big Egg Marsh Experimental Saltmarsh Restoration Project, for which Mr. Adamo provided administrative assistance and began shortly after he reported to Gateway. In a multi-agency effort over the past 13 months, Mr. Adamo worked on compliance, alternative, and monitoring issues for the proposed Elder’s Point and Yellow Bar Saltmarsh Restoration Project sponsored by the U.S. Army Corps of Engineers, New York City Department of Environmental Protection, and the Port Authority of NY & NJ. Mr. Adamo also serves on the Harbor Estuary Program’s Management Committee and the Long-Term Control Planning Government Steering Committee, both of which involve considerable efforts toward improving water quality in Jamaica Bay. In addition, he has coordinated development of and sought funding for several National Park Service project proposals to restore ecosystem health to Jamaica Bay. In April 2005, he hosted the first symposium on oysters and eelgrass in Jamaica Bay. Mr. Adamo has a B.S. in Wildlife Biology and M.S. in Soil Science from West Virginia University. He previously worked as a biologist for the U.S. Fish and Wildlife Service, U.S. Army Corps of Engineers, and the U.S. Forest Service. Manny Caughman A community and environmental activist, Manuel Caughman is an active member of the Queens community, whose contributions in helping to resolve the environmental issues facing the residents of Southeast Queens has been evident for over almost a decade. As Chairman of the Community Board #12 Environmental Committee, the 29th Assembly District Environmental Committee, and a member of the Brooklyn-Queens Aquifer Feasibility Study, he has been instrumental in bringing attention to and resolving the issues currently facing the residents of Southeast Queens. Having received numerous awards for his dedication to environmental issues pertaining to water quality, soil contamination and protection of aquifers, Mr. Caughman is recognized in the community by residents and elected officials on every level of government as a respected authority on issues facing the environment. The remediation of the West Side Hazardous Waste Site was paramount in improving environmental issues by removing petrochemicals from the soil that could possibly contaminate the aquifers. Mr. Caughman is currently working along with city and elected officials to address the rising water table affecting Southeastern Queens. Len Houston Len Houston is Chief of the Environmental Analysis Branch for the U.S. Army Corps of Engineers, New York District. He holds a B.S. in Biology from Brooklyn College and a M.S. in Marine Biology from Long Island University. Mr. Houston authored the Reconnaissance Report (1999) recommending that the Federal government undertake (with the New York City Department of Environmental Protection as partner) preparation of a Feasibility Study for Environmental Improvements to Jamaica Bay. He was the Team Leader who developed the Jamaica Bay Environmental Survey that identified 50-plus potential improvement options,
2
and developed a scope of work and funding transfers for extensive field studies to investigate and assess many of those sites as part of the Jamaica Bay Ecosystem Restoration Program field study undertaken by the Aquatic Research and Environmental Assessment Center (AREAC) at Brooklyn College (under oversight and guidance of the Gateway National Recreation Area). As Chief of the Special Studies Section, Mr. Houston worked with the New York City Parks and Recreation Department to initiate and complete studies for environmental restoration projects at Gerritsen Beach and Spring Creek, the former of which was completed and led to the signing of a Project Cooperation Agreement with the City Parks Department to construct the recommended marsh restoration project upon appropriation of Federal studies. As Branch Chief, he worked with Gateway, the New York State Department of Environmental Conservation, Port Authority of NY & NJ and the New York City Department of Environmental Protection to initiate a study for a pilot project at Elders Point and Yellow Bar to address marsh island losses in Jamaica Bay. The Elders Point project has been funded and a contract to restore the mostly eroded marsh using stockpiled sand from the maintenance of Rockaway Inlet was awarded and is scheduled for completion in summer 2006. Mr. Houston is the author of several presentations on restoration needs/options in Jamaica Bay for conferences sponsored by Gateway and AREAC. He is the Corps representative to the Jamaica Bay Task Force. Dan Mundy Dan Mundy is a retired Fire Captain and a lifelong resident of Broad Channel, Queens. In 1995 he was the first to notice the disappearance of the marshes in Jamaica Bay and in 1996 founded the Jamaica Bay Eco Watchers, an environmental group advocating for the restoration and funding to protect this great resource. He is the environmental chairperson of Community Board #14 and also serves on citizens advisory committees for the Harbor Estuary Program and Pollution Control. Mr. Mundy has been active in the planning, construction, and monitoring of the Big Egg Marsh Restoration project as well as the next restoration project with the U.S. Army Corps of Engineers, New York State Department of Environmental Conservation and New York City Department of Environmental Protection. Eco Watchers also conducts water quality monitoring and works closely with other scientists working in Jamaica Bay. For the past four years, Mr. Mundy has led Operation Clean Sweep, a cooperative effort with the National Park Service, New York Department of Environmental Conservation, New York Department of State, Port Authority of NY & NJ, the New York Police Department, and the Jamaica Bay Guardian in removing hundreds of derelict boats and debris from the water and marshes of Jamaica Bay. Bradford H. Sewell Bradford H. Sewell is a senior attorney with the Natural Resources Defense Council, Inc. (NRDC), a public interest organization specializing in environmental protection. He is Director of the NRDC NY/NJ Harbor-Bight Project, which focuses on NY/NJ marine environmental issues, including marine water quality and fisheries. Since 1998, Mr. Sewell has also served as Director of the NRDC Everglades Project. NRDC has been working to reduce the impacts on Jamaica Bay of combined sewer overflows and nitrogen pollution from New York City’s wastewater treatment facilities. NRDC also provided legal assistance in the creation of Gateway National Recreation Area. Other relevant areas of NRDC’s ongoing work include the clean up of contaminated sediments in Newark Bay (including minimizing impacts of navigational dredging projects), clean up of Hudson River PCBs, preserving the Hackensack Meadowlands, coastal habitat preservation around New York City, and green building design in the City. NRDC annually publishes Testing the Waters, which details the problem of beach closings as a result of
3
water pollution; also, in 2002, NRDC published a report entitled Cape May to Montauk: A Coastal Protection Report Card. Mr. Sewell has a bachelor's degree from Stanford University, a law degree from Columbia University, and a master's in public health from the Division of Environmental Sciences at Columbia's School of Public Health. He is an adjunct faculty member at Columbia University School of Public Health, Division of Environmental Sciences. From 1992-1998, Mr. Sewell was an attorney at the New York law firm of Paul, Weiss, Rifkind, Wharton and Garrison, where he litigated and counseled clients concerning environmental matters. Dr. R. Lawrence Swanson Dr. R. Lawrence Swanson received his Ph.D. in Physical Oceanography from Oregon State University in 1971. Since 1987, he has been the director of the Waste Reduction and Management Institute (WRMI), and since 2003 also the Associate Dean of the Marine Sciences Research Center, Stony Brook University (SBU). Prior to his appointment at SBU, he was with the National Oceanic and Atmospheric Administration and served in a variety of capacities including Project Manager of the Marine Ecosystems Analysis Program for the New York Bight; Director of the Office of Marine Pollution Assessment; and the Executive Director of the Office of Oceanic and Atmospheric Research.
Dr. Swanson plays an active role in New York City’s marine policy, often testifying at public hearings and producing government reports and policy recommendations. He has conducted research on water quality, ocean dumping, marine debris and medical wastes, hypoxia, marine pollution issues, and waterfront uses in and around New York City. Dr. Swanson serves as the principal investigator on the New York State component of the National Coastal Assessment Program, where he coordinates sampling of water quality, sediment toxicity and biological health of New York waters, including specific sites in Jamaica Bay. He also served as co-editor of a National Oceanic and Atmospheric Administration book concerning hypoxia and mass mortalities in the New York Bight. Dr. Swanson’s work contributed to passage of federal legislation and also led to the national emphasis on regulating combined sewer overflows. More recently, he synthesized large data sets for the New York City Department of Environmental Protection in order to expand the utility of the City’s annual water quality monitoring program. This past year, he, along with other members of his research team, published a monitoring plan for the Hudson River for the New York State Department of Environmental Conservation. Swanson and a colleague, R.E. Wilson, have also prepared a paper for publication synthesizing historical data sets as they pertain to hypoxia in Western Long Island Sound. Christopher R. Zeppie Christopher R. Zeppie is Director of the Office of Environmental Policy, Programs and Compliance at the Port Authority of New York and New Jersey. Since coming to the Port Authority in 1979, Mr. Zeppie has held positions of increasing responsibility as Environmental Compliance Specialist; Manager, Permits and Governmental Approvals; Attorney, Environmental Law Division; Assistant Director, Office of Environmental Management; and Chief Environmental Policy Officer. Mr. Zeppie serves on the Transportation Research Board’s Committee on Climate Change and U.S. Transportation as well as the Steering Committee of the Environmental Division of the New York Academy of Sciences, the Advisory Committee to New York State Sea Grant, and the New York State Implementation Plan Coordinating Council for the Federal Clean Air Act.
4
He holds a B.S. degree in biology and ecology from Manhattan College, a M.S. degree in marine environmental science from the Marine Sciences Research Center at Stony Brook, and a J.D. degree from St. John’s University School of Law. His Master Thesis is entitled “Vertical Profiles and Sedimentation Rates of Cd, Cr, Cu, Ni and Pb in the Sediments of Jamaica Bay, New York,” and entailed extensive research in and around Jamaica Bay. Prior to coming to the Port Authority, Mr. Zeppie worked as an Oceanographer at the New York District Corps of Engineers, Water Quality Compliance Branch and he has also held the position of environmental engineer at the New York Power Authority. He has been an adjunct faculty member at Stony Brook and the New York Institute of Technology. Mr. Zeppie lives on Long Island in Rockville Centre and has three children and one grandchild.
Appendix E
LIST OF EXPERT PANELS CONVENED BY THE ADVISORY COMMITTEE To help advise their recommendations, the Advisory Committee requested that a number of agency representatives and scientists who have conducted research concerning the Bay or have expertise in certain key areas address the committee. Below please find a list of speakers and the general topics they were asked to address. May 15 Panel Discussion Topic: “What is the water quality like in Jamaica Bay and how can it be improved?” Panelists:
• Robert Wilson, Ph.D., Stony Brook University • Mark Ringenary, Water Quality Specialist, Division of Natural Resources, Gateway NRA
Martin P. Schriebman, Ph.D., Founding Director of the Aquatic Research and Environmental Assessment Center, Brooklyn College
• Anne McElroy, Ph.D., Stony Brook University
April 26 Panel Discussion Topic: “What measures can we take to reverse wetlands loss in Jamaica Bay and restore wetlands?” Panelists:
• Dr. Alex Kolker, Ph.D., Stony Brook University • Charles Roman, Research Coordinator for the National Park Service, North Atlantic
Coast Cooperative Ecosystem Studies Unit • Steve Zahn, Marine Resources Program Manager, New York State Department of
Environmental Conservation, Region 2 March 22 Panel Discussion Topic: “How could we adopt more green infrastructure and other stormwater best management practices into the Jamaica Bay watershed?” Panelists:
• Paul Mankiewicz, Ph.D., Executive Director, The Gaia Institute • Neil Weinstein, Executive Director, Low Impact Development Center
Appendix F
1
LIST OF WATERSHED PROTECTION PLAN GOALS
Secure fishable/swimmable waters in Jamaica Bay. Meet or exceed current federal, state, and local water quality standards for Jamaica Bay’s open water and
tributaries. Attaining these standards would at least ensure water suitable for secondary recreation (e.g. kayaking, fishing) in most of Jamaica Bay’s waters, and primary recreation (e.g. swimming, shellfishing) in the bay’s open waters.
Significantly reduce the frequency and severity of harmful algal blooms in Jamaica Bay’s open waters resulting from anthropogenic influences.
Reduce inputs of nitrogen and organic substances into Jamaica Bay to levels necessary to achieve numeric water quality criteria for dissolved oxygen (5.0 milligrams/Liter) throughout Jamaica Bay’s open waters.
Significantly reduce combined sewer overflows (CSOs) with the goal of eliminating all CSOs into Jamaica Bay (including tributaries) by 2020.
Significantly reduce harmful impacts from soil and sediment contamination in Jamaica Bay.
No localized or net increase in contaminant concentrations in sediments and soils within Jamaica Bay watershed as a result of inputs via groundwater, combined sewer overflows, and water pollution control plant effluents.
Significantly reduce or reverse acute and chronic detrimental biological and ecological impacts from sediment and soil contamination within the Jamaica Bay watershed, focusing on known bioaccumulative agents, such as heavy metals and certain organic compounds.
Identify and monitor location and nature of sediment contamination in Jamaica Bay watershed. Prioritize remediation of sites containing sediments and/or soils identified as posing a human and/or ecological risk.
Restore populations of oysters and other shellfish to Jamaica Bay.
Eliminate floatables, debris, slicks and settleable solids in Jamaica Bay to create a healthy, trash-free
recreation area. Eliminate discharge of CSO settleable solids into Jamaica Bay. Remove CSO sediment deposits to help restore healthy marine ecosystems. Identify and remove existing debris causing ecological or aesthetic impairment.
Prevent additional loss, in quality and extent, of existing Jamaica Bay wetland and maritime native
habitat complexes, including those serving as upland buffers, and increase the spatial extent of these habitats.
Protect Jamaica Bay’s inner salt marsh complexes from additional loss of spatial extent and function,
and increase the spatial extent of these marsh complexes.
Prevent the introduction or spread of ecologically harmful invasive plant and animal species in and around Jamaica Bay, and reduce their current distribution and population levels as appropriate to improve natural diversity and ecological functions of the Bay.
Ensure a diverse and healthy population of native flora and fauna in Jamaica Bay.
Institute an ongoing Jamaica Bay monitoring/science research program that identifies additional
scientific needs, and coordinates interagency research and monitoring.
Improve public awareness of and access to Jamaica Bay. Develop education and outreach programs to increase knowledge of Jamaica Bay, including the benefits it
provides the public, in adjacent communities and in the city as a whole. Increase the number of public access points to Jamaica Bay. Increase awareness of Jamaica Bay and its public benefits among elected officials.
Appendix G
LOCAL LAWS
OF
THE CITY OF NEW YORKFOR THE YEAR 2005
No. 86
Introduced by The Speaker (Council Member Miller) and Council Members Gennaro, Brewer, Clarke, Fidler, Gerson, Gioia, James, Koppell, Liu, Martinez, Nelson, Recchia, Sanders, Stewart, Weprin, Gonzalez, Yassky, Moskowitz, Reyna, Foster, Perkins, McMahon, Addabbo Jr., Monserrate, Gentile, DeBlasio, Baez, Palma, Katz, Avella, Reed, Jackson, Vallone, Jr., Quinn, Rivera, Barron, Lopez, Arroyo, Sears and The Public Advocate (Ms. Gotbaum).
A LOCAL LAW
To amend the New York city charter, in relation to green building standards for
certain capital projects.
Be it enacted by the Council as follows:
Section 1. Statement of findings and purpose. Probably no urban activity has greater impact on human health and the environment than building construction and use. Enormous quantities of resources are used during building construction, renovation and operation, and the production of these resources has substantial environmental impacts. It is estimated that 40% of raw materials consumed globally are used for buildings. In addition, in the United States, commercial and residential buildings are responsible for approximately 65% of electricity consumption, 30% of greenhouse gas emissions, 12% of potable water use and 136 million tons of construction and demolition waste annually. Also, many indoor building materials release hazardous toxins, impairing indoor air quality and reducing occupant health and productivity.
Since most of New York City’s electricity is produced within the City and many buildings use oil or natural gas for their heating and hot water, energy consumption in building operation translates into greater local pollution, including emissions of sulfur dioxide, nitrogen oxides, particulate matter, carbon dioxide, and mercury. These pollutants contribute to respiratory disease, heart disease, smog, acid rain, and climate change. Moreover, as energy demand rises, so does our reliance on dirty, inefficient power plants, as well as the nation’s dependence on foreign oil and natural gas.
Modern architects and engineers can reduce the health and environmental impacts of buildings by designing “high-performance buildings” or “green buildings.” The United States Green Building Council, the nation’s foremost coalition of real estate and environmental organizations working to promote green buildings, has developed a green building rating system known as LEED (Leadership in Energy and Environmental Design). Buildings receive LEED certification if their designs score sufficient "points"
2 in five general design areas including siting, water efficiency, energy and atmosphere, materials and resources and indoor environmental quality. Thousands of residential and commercial buildings, ranging from single-family homes to large corporate headquarters, have been designed and constructed throughout the United States utilizing green building principles. Significant local examples include 4 Times Square and 20 River Terrace. A recent study conducted for the State of California concluded that, on average, green buildings show a ten times return on the investment in green building design. This comprehensive analysis of 33 green buildings revealed an average green cost premium of less than 2%, with only a 0.66% premium for buildings that achieved the most basic level of LEED certification.
Numerous municipalities, including Atlanta, Austin, Boston, Boulder, Chicago, Dallas, Los Angeles, Portland (Oregon), San Diego, San Francisco, San José, and Seattle, have adopted LEED or have otherwise required that city-owned buildings be built according to green building criteria. Some localities have created incentive programs for privately-owned green building construction, including the use of direct subsides, density bonuses and expedited permitting. Indeed, Boston will soon require private sector buildings of over 50,000 square feet to be LEED-certifiable.
In New York City, numerous governmental bodies have also embraced green building concepts. The Battery Park City Authority has begun utilizing green building guidelines modeled on LEED for all commercial and residential building construction in Battery Park City. The Department of Design and Construction has also developed High Performance Building Guidelines and has begun applying the guidelines for libraries and other facilities. The New York City Transit Authority has adopted green building guidelines for all new transit facilities, including the Second Avenue Subway. Moreover, the Lower Manhattan Development Corporation and the Port Authority of New York and New Jersey have developed sustainable design guidelines and have designated “environmental planning” as one of five general requirements for the redevelopment of the World Trade Center site and surrounding area.
Likewise, many states, such as California, Connecticut, Maryland, Massachusetts, New Jersey, New York, Pennsylvania, and Rhode Island, have begun utilizing LEED for state-owned buildings. The State of New York provides tax credits for buildings that meet defined green building criteria and, under Executive Order 111, state agencies are directed to reduce energy use and carbon dioxide emissions and to utilize green building principles.
The City owns approximately 1,300 buildings and leases over 12.8 million square feet of office space, and this legislation will affect approximately $12 billion in construction over the City’s ten-year capital plan. Considering the size of the City’s real estate portfolio, the Council finds that the use of green building criteria for City capital projects will substantially reduce New York City’s electricity consumption, air pollution and water use, as well as improve occupant health and worker productivity and encourage market transformation. The Council further finds that reducing overall energy demand through green building techniques will reduce our dependence on foreign oil. Finally, the Council finds that green buildings are a sound investment of public dollars. The Council’s financial analysis indicates that, without taking any other savings or social benefits into account, savings in water and energy cost will offset debt service payments on any increase in capital expenditures resulting from this legislation. Accordingly, the Council declares that it is reasonable and necessary to employ green building standards in the construction and renovation of City-owned and City-funded buildings and that these standards be utilized in an orderly and timely fashion.
3 §2. The New York city charter is amended by adding a new section 224.1, to read as
follows: §224.1 Green building standards. a. As used in this section the following terms
shall have the following meanings: (1) The term “capital project” shall mean a capital project as defined in section
210 of this chapter that is paid for in whole or in part from the city treasury. (2) The term “city agency” shall mean a city, county, borough, or other office,
position, administration, department, division, bureau, board or commission, or a corporation, institution or agency of government, the expenses of which are paid, in whole or in part, from the city treasury.
(3) The term “construction work” shall mean any work or operations necessary or incidental to the erection, demolition, assembling, alteration, installing, or equipping of any building.
(4) The term “green building standards” shall mean design guidelines, a rating system or rules for constructing buildings that ensure site planning, water efficiency, energy efficiency and renewable energy, conservation of materials and resources and indoor environmental quality.
(5) The term “inflation” shall mean the annual twelve (12) month average of the consumer price index published by the United States department of labor.
(6) The term “LEED energy and atmosphere credit 1” shall mean the credit point under LEED for New Construction version 2.1 intended to achieve increased energy performance.
(7) The term "LEED green building rating system" shall mean a version of the Leadership in Energy and Environmental Design (LEED) building rating system published by the United States Green Building Council, not less stringent than the selected green building rating system, including a standard developed by or for the city consisting of practices and technologies derived from the LEED rating system that are reasonable and appropriate for building in New York city.
(8) The term “LEED water efficiency credit 3.2” shall mean the credit point under the LEED for New Construction version 2.1 intended to achieve water use reduction.
(9) The term “not less stringent” shall mean providing no less net environmental and health benefits.
(10) The term “rehabilitation work” shall mean any restoration, replacement or repair of any materials, systems and/or components.
(11) The term “selected green building rating system” shall mean the current and most appropriate building rating system published by the United States Green Building Council; provided, however, at the mayor’s discretion, the term “selected green building rating system” shall mean New Construction version 2.1, Existing Buildings version 2 or Commercial Interiors version 2, whichever is most appropriate for the project under United States Green Building Council guidelines.
(12) The term “substantial reconstruction” shall mean a capital project in which the scope of work includes rehabilitation work in at least two of the three major systems, electrical, HVAC (heating, ventilating and air conditioning) and plumbing, of a building and construction work affects at least fifty percent (50%) of the building’s floor area.
b. (1) Each capital project with an estimated construction cost of two million dollars ($2,000,000) or more involving (i) the construction of a new building, (ii) an addition to an existing building, or (iii) the substantial reconstruction of an existing building shall be designed and constructed to comply with green building standards not less stringent than the standards prescribed for buildings designed in accordance with
4 the LEED green building rating system to achieve a LEED silver or higher rating, or, with respect to buildings classified in occupancy groups G or H-2, to achieve a LEED certified or higher rating. If the mayor elects to utilize green building standards other than the LEED green building rating system, the mayor shall publish findings demonstrating that such other green building standards are not less stringent than the LEED standards described above for achievement of a LEED silver or, if applicable, a LEED certified rating. The green building standards utilized by the city in accordance with this section shall be reviewed and updated, as necessary, by the mayor no less often than once every three years.
(2) In addition, if the estimated construction cost of a project required to comply with green building standards in accordance with paragraph one of this subdivision is 12 million dollars ($12,000,000) or more such project shall be designed and constructed to reduce energy cost as follows:
(i) Capital projects, other than buildings classified in occupancy group G, with an estimated construction cost of 12 million dollars ($12,000,000) or more but less than 30 million dollars ($30,000,000) shall be designed and constructed to reduce energy cost by a minimum of twenty percent (20%), as determined by the methodology prescribed in LEED energy and atmosphere credit 1 or the New York state energy conservation code, whichever is more stringent. In addition to such twenty percent (20%) reduction in energy cost, the design agency shall make investments in energy efficiency that reduce energy cost by an additional five percent (5%) if it finds that the payback on such investment through savings in energy cost would not exceed seven years.
(ii) Capital projects, other than buildings classified in occupancy group G, with an estimated construction cost of 30 million dollars ($30,000,000) or more shall be designed and constructed to reduce energy cost by a minimum of twenty-five percent (25%), as determined by the methodology prescribed in LEED energy and atmosphere credit 1 or the New York state energy conservation code, whichever is more stringent. In addition to such twenty-five percent (25%) reduction in energy cost, the design agency shall make investments in energy efficiency that reduce energy cost by an additional five percent (5%) if it finds that the payback on such investment through savings in energy cost would not exceed seven years.
(iii) Capital projects involving buildings classified in occupancy group G with an estimated construction cost of 12 million dollars ($12,000,000) or more shall be designed and constructed to reduce energy cost by a minimum of twenty percent (20%), as determined by the methodology prescribed in LEED energy and atmosphere credit 1 or the New York state energy conservation code, whichever is more stringent. In addition to such twenty percent (20%) reduction in energy cost, the design agency shall make investments in energy efficiency that reduce energy cost by an additional five percent (5%) if it finds that the payback on such investment through savings in energy cost would not exceed seven years or, in the alternative, the design agency shall make investments in energy efficiency that reduce energy cost by an additional ten percent (10%) if it finds that the payback on such investment through savings in energy cost would not exceed seven years.
c. Capital projects, other than those required to comply with green building standards in accordance with subdivision b of this section, shall be subject to the following:
(1) Each capital project that includes the installation or replacement of a boiler at an estimated construction cost for such installation or replacement of two million dollars ($2,000,000) or more, or that involves the installation or replacement of lighting systems
5 in a building at an estimated construction cost for such installation or replacement of one million dollars ($1,000,000) or more, shall be designed and constructed to reduce energy cost by a minimum of ten percent (10%), as determined by the methodology prescribed in LEED energy and atmosphere credit 1 or the New York state energy conservation code, whichever is more stringent.
(2) Each capital project, other than a project required to comply with paragraph one of this subdivision, that involves the installation or replacement of HVAC comfort controls at an estimated construction cost for such installation or replacement of two million dollars ($2,000,000) or more, shall be designed and constructed to reduce energy cost by a minimum of five percent (5%) as determined by the methodology prescribed in LEED energy and atmosphere credit 1 or the New York state energy conservation code, whichever is more stringent.
d. In addition to complying with any other applicable subdivision in this section, each capital project involving the installation or replacement of plumbing systems that includes the installation or replacement of plumbing fixtures at an estimated construction cost for such installation or replacement of plumbing systems of five hundred thousand dollars ($500,000) or more shall be designed and constructed to reduce potable water consumption in the aggregate by a minimum of thirty percent (30%), as determined by a methodology not less stringent than that prescribed in LEED water efficiency credit 3.2; provided, however, that such percentage shall be reduced to a minimum of 20% if the department of buildings rejects an application for the use of waterless urinals for the project.
e. This section shall apply only to capital projects involving buildings classified in occupancy groups B-1, B-2, C, E, F-1a, F-1b, F-3, F-4, G, H-1 and H-2.
f. The mayor may exempt from each provision of this section capitol projects accounting for up to 20% of the capital dollars in each fiscal year subject to such provision if in his or her sole judgment such exemption is necessary in the public interest. At the conclusion of each fiscal year the mayor shall report to the council the exemptions granted pursuant to this section.
g. This section shall not apply to capital projects of entities that are not city agencies unless fifty percent (50%) or more of the estimated cost of such project is to be paid for out of the city treasury. This exemption shall not apply to any capital project that receives ten million dollars ($10,000,000) or more out of the city treasury.
h. This section shall not apply to capital projects that have received capital dollars from the city treasury before January 1, 2007.
i. The mayor shall promulgate rules to carry out the provisions of this section. j. The costs listed in subdivisions b, c, d and g of this section shall be indexed to
inflation. k. Capital projects accounting for at least fifty percent (50%) of the capital dollars
in each fiscal year allocated for each city agency that are subject to paragraph one of subdivision b of this section that utilize a version of the LEED green building rating system for which the United States Green Building Council will accept applications for certification, shall apply to the United States Green Building Council for certification that such projects have achieved a silver or higher rating under the LEED green building rating system or, with respect to projects involving buildings classified in occupancy groups G or H-2, a certified or higher rating under such rating system.
§3. An annual report shall be prepared no later than September 1 of each year in accordance with the procedure and format established by the department of design and construction. Such report shall include, but shall not be limited to, a list and brief
6 description, including square footage and total cost, of any capital project subject to section 224.1 of the charter, as added by section 2 of this local law, completed during the preceding calendar year; the estimated level of LEED certification such capital projects have achieved as determined by the design agency in accordance with the LEED rating system or, if applicable, the level achieved, as certified by the United States Green Building Council; additional costs attributable to complying with the LEED green building rating system or any other green building standard; an assessment of the health, environmental and energy-related benefits achieved in comparison with a base-case code compliant project (including projected energy savings and reductions in peak load, reductions in emissions, reductions in storm water runoff and potable water use); a summary of agency findings related to additional investment in energy efficiency pursuant to subparagraphs (i), (ii), and (iii) of paragraph two of subdivision b of section 224.1 of the charter, including any additional investment in energy efficiency considered and the estimated payback time for such investment through savings in energy cost; and the total value of capital allocations in each fiscal year, by city agency, of projects subject to, and exempted by the mayor for each of paragraph one and subparagraphs (i), (ii) and (iii) of paragraph two of subdivision b, paragraphs one and two of subdivision c and subdivision d of section 224.1 of the charter, as added by section 2 of this local law, as well as a list and brief description, by agency, of such exempted projects, including square footage and project cost. The first such report shall be completed on or prior to September 1, 2008.
§4. This local law shall take effect on January 1, 2007 and shall apply to capital projects for which the final design is approved pursuant to section 223 of the New York city charter after such effective date, except that prior to such effective date the mayor shall take all actions necessary for the timely implementation of this local law, including the promulgation of rules, and shall take all practicable steps to implement this local law. Section 3 of this local law shall expire and shall be of no further force and effect on and after January 1, 2019. Subdivision k of section 224.1 of the charter, as added by section 2 of this local law, shall expire and shall be of no further force and effect on and after January 1, 2017.
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THE CITY OF NEW YORK, OFFICE OF THE CITY CLERK, s.s.: I hereby certify that the foregoing is a true copy of a local law of the City of New
York, passed by the Council on September 15, 2005, and approved by the Mayor on October 3, 2005.
VICTOR L. ROBLES, City Clerk of the Council
CERTIFICATION PURSUANT TO MUNICIPAL HOME RULE LAW §27 Pursuant to the provisions of Municipal Home Rule Law §27, I hereby certify that
the enclosed Local Law (Local Law 86 of 2005, Council Int. No. 324-A) contains the correct text and:
Received the following vote at the meeting of the New York City Council on September 15, 2005: 46 for, 0 against, 0 not voting.
Was signed by the Mayor on October 3, 2005. Was returned to the City Clerk on October 4, 2005.
JEFFREY D. FRIEDLANDER, Acting Corporation Counsel
Appendix H
Appendix I
LOCAL LAWS
OF
THE CITY OF NEW YORKFOR THE YEAR 2005
No. 83
Introduced by Council Members Gennaro, Addabbo Jr., Avella, Comrie, Fidler, Gerson, Gonzalez, Jennings, Koppell, Lopez, Martinez, McMahon, Palma, Quinn, Recchia, Sanders, Weprin, Reyna, Monserrate, Lanza, Vallone Jr., Brewer, Yassky, Gentile, Liu, Jackson, Gallagher, DeBlasio, Arroyo and the Public Advocate (Ms. Gotbaum).
A LOCAL LAW
To create a temporary task force to study the feasibility of transferring city-owned
wetlands to the jurisdiction of the department of parks and recreation.
Be it enacted by the Council as follows:
Section 1. Legislative findings and intent. Wetlands are among the most productive ecosystems in the world. For example, wetlands such as intertidal or salt marshes are comparable in ecological productivity to rainforests. An immense variety of species of microbes, plants, insects, amphibians, reptiles, birds, fish and mammals can be part of a wetland ecosystem. Physical and chemical features such as climate, landscape shape, geology and the movement and abundance of water help to determine the plants and animals that inhabit a wetland. Wetlands provide values that no other ecosystem can, including natural water quality improvement, flood protection, shoreline erosion control and opportunities for recreation and aesthetic appreciation. In the City of New York, there are approximately fourteen square miles of wetlands still in existence, where more than 100 square miles once existed. Despite urbanization, 778 native plants and animals still exist in the City, accounting for sixty percent of the species that existed 100 years ago.
A number of inventories regarding wetland areas in New York City already exist, such as those included in recommendations of the Habitat Working Group of the Harbor Estuary Program; recommendations of “An Islanded Nature”, the latest report on expanding the Harbor Herons Urban Nature Refuge concept; the recommendations of the Needs and Opportunities Report to the Army Corp of Engineers on environmental restoration of the harbor estuary; and, the recommendations of the Regional Plan Association. In addition, there may be other inventories in existence that are not included in the above-mentioned list.
An outstanding example of wetlands with ecological, water quality improvement, and recreational and aesthetic significance is those found in or near Jamaica Bay. This bill would create a task force to inventory City-owned wetlands in the City of New York
2 and ascertain the feasibility of transferring these properties to be under the protection of the Department of Parks and Recreation.
The City Council finds that City-owned wetlands, for which a transfer to the Department of Parks and Recreation is feasible, should be transferred in an expeditious manner in order to protect and maintain their environmental, economic and other benefits to New York City.
§2. a. There is hereby established a temporary task force to advise the mayor of the city of New York and the speaker of the council of the city of New York as to the technical, legal, environmental and economical feasibility of a transfer of city-owned wetland areas, including, but not limited to, those listed in existing inventories, to the department of parks and recreation.
b. Such task force shall be comprised of seven members, three of whom shall be appointed by the speaker of the council and four by the mayor. The members shall be appointed within sixty days of the enactment of this local law and shall serve without compensation. The chairperson shall be elected from amongst the members. Any vacancy shall be filled in the same manner as the original appointment for the remainder of the unexpired term. The commissioners of environmental protection and parks and recreation may provide staff to assist the task force.
c. Such members of the task force shall serve for a period of nine months, after which time such task force shall cease to exist.
d. No later than three months before the expiration of the task force, the chairperson shall submit a report containing its conclusions and recommendations to the mayor of the city of New York and the speaker of the council of the city of New York.
e. No later than six months after the submission of the report pursuant to subdivision d of this section, the mayor of the city of New York, or his or her designee, shall submit a report to the speaker of the council of the city of New York, which shall include, of those city-owned wetland areas that the task force deemed feasible for transfer to the department of parks and recreation:
1. the wetland areas that were transferred to such department, including the dates upon which such transfers occurred;
2. the wetland areas that are in the process of being transferred to such department or for which a determination to transfer has been made but for which the process to transfer has not yet begun, including the status of and anticipated dates for such transfers; and
3. the wetland areas that were not transferred and are not in the process of being transferred to such department, including an explanation as to why such action was not or will not be taken.
§3. This local law shall take effect immediately upon its enactment.
3
THE CITY OF NEW YORK, OFFICE OF THE CITY CLERK, s.s.: I hereby certify that the foregoing is a true copy of a local law of the City of New
York, passed by the Council on August 17, 2005, and approved by the Mayor on August 31, 2005.
VICTOR L. ROBLES, City Clerk of the Council
CERTIFICATION PURSUANT TO MUNICIPAL HOME RULE LAW §27 Pursuant to the provisions of Municipal Home Rule Law §27, I hereby certify that
the enclosed Local Law (Local Law 83 of 2005, Council Int. No. 566-A) contains the correct text and:
Received the following vote at the meeting of the New York City Council on August 17, 2005: 47 for, 0 against, 0 not voting.
Was signed by the Mayor on August 31, 2005. Was returned to the City Clerk on September 1, 2005.
JEFFREY D. FRIEDLANDER, Acting Corporation Counsel